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pMJFORNIA 

FISH-GAME 


VOLUME  46 


JULY,  1960 


NUMBER  3 


California  Fish  and  Game  is  o  journal  devoted  to  the  conserva- 
tion of  wildlife.  Its  contents  may  be  reproduced  elsewhere  pro- 
vided credit  is  given  the  authors  and  the  California  Department 
of  Fish  and  Game. 

The  free  mailing  list  Is  limited  by  budgetary  considerations  to 
persons  who  con  make  professional  use  of  the  material  and 
to  libraries,  scientific  institutions,  and  conservation  agencies.  Indi- 
viduals must  state  their  affiliation  and  position  when  submitting 
their  applications.  Subscriptions  must  be  renewed  annually  by 
returning  the  postcard  enclosed  with  each  October  issue.  Sub- 
scribers are  asked  to  report  changes  in  address  without  delay. 

Please  direct  correspondence  to: 

CAROL  M.  FERREL,  Edifor 
Department  of  Fish  and  Game 
722  Capitol  Avenue 
Sacramento  14,  California 

Individuals  and  organizations  who  do  not  qualify  for  the  free 
mailing  list  may  subscribe  at  a  rate  or  $2  per  year  or  obtain  indi- 
vidual issues  for  $0.75  per  copy  by  placing  their  orders  with  the 
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Money  orders  or  checks  should  be  made  out  to  Printing  Division, 
Documents  Section. 


u 


I] 


V 


VOLUME  46 


JULY,   1960 


NUMBER  3 


Published  Quarterly  by  the 

CALIFORNIA  DEPARTMENT  OF  FISH  AND  GAME 

SACRAMENTO 


STATE   OF   CALIFORNIA 

DEPARTMENT  OF  FISH  AND  GAME 


EDMUND  G.   BROWN 
Governor 


FISH   AND  GAME  COMMISSION 

WILLIAM   P.    ELSER,  President 
San  Diego 

JAMIE   H.   SMITH,  Vice  President  T.    H.    RICHARDS,   JR.,  Commissioner 

Los  Angeles  Sacramento 

CARL   F.   WENTE,  Commissioner  HENRY   CLINESCHMIDT,  Commissioner 

San  Francisco  Redding 


WALTER  T.   SHANNON 
Director  of  Fish  and  Gome 


CALIFORNIA  FISH  AND  GAME 
Editorial  Staff 

CAROL    M.     FERREL,     Editor-in-Chief Sacramento 

JOHN    E.    FITCH,    Editor   for   Marine    Resources   Terminal    Island 

ELTON    D.    BAILEY,    Editor   for    Inland    Fisheries    Sacramento 

MERTON    N.    ROSEN,    Editor    for    Game Sacramento 

DONALD   H.   FRY,  JR.,   Editor  for   Salmon  and   Steelhead  Sacramento 


TABLE  OF   CONTENTS 

Page 
TIk^  Wood  Duck  in  California  with  Special  Reference  to  the  Use 

of  Xest  Boxes A.  E.  Naylor     241 

Use  of  Desert  Slirnhs  by  Jackrabbits  in  Northeastern  California 

Sturfjis  McKecvcr  and  Richard  L.  Hubbard     271 

The  A<ie  and  (Irowth  of  Striped  Bass  (Roccus  saxatilis)  in 

California John  B.  Robinson     27!) 


The  Ini]iortance  of  the  Ocean  Sport  Fishery  to  the  Ocean  ('atch 

'gon  and  California 
Henri/  ().  Wmdlrr     2!)1 


of  Salmon  in  the  States  of  Washington,  Oregon  and  (California 


Tuna  Ta-iging'  in  the  Eastei-n  Ti-opical   Pacific,  l!)r)2-ir)5r) 

C.  E.  Blunt.  Jr.  and  James  D.  Messersinifh     :!()1 

Note 

Toxicity  of  Ti'icon  ()il  Spill  Eradicatoi-  to  Striped  Bass  (Roccns 
saxatilis) Harold   I\ .   Chadn-icl:     ■}^^ 

Note 

A  Rano'e  Extension  of  the  Crdifoi-nia  llfdibut  (Paralickthys 

californicKs) E.    G.    (inndcrson     873 

Reviews   375 


(  239  ) 


THE  WOOD   DUCK   IN   CALIFORNIA  WITH   SPECIAL 
REFERENCE  TO  THE   USE  OF   NEST   BOXES' 

A.    E.    NAYLOR 

Game  Management  Branch 

California  Department  of  Fish  and  Gome 

INTRODUCTION 

Asidi'  I'roiii  Jiiiiitiim'  scnsoii  fcsl  I'ict  ions,  llicrc  luis  been  lilllc  cn'orl 
(lui'iiii;-  Ihc  I;is1  luilf  (-cntui-y  hciil  lowjird  tlii'  sliuly  and  iii<ina<i'('iiu'iit  of 
tlu'  wood  duck  (^ii.r  spoiisa)  in  ('aliroi'nia.  The  wood  diu-k  now  holds 
a  position  of  secondary  inipoi'taiicc  witliiii  llic  Slate.  'I'lus  is  due  to  tlie 
rathef  linnted  population  and  to  the  haii'  limit  I'cst  i-id  ion  of  one  bii'd, 
two  factors  wliicli  reduce  its  utility  as  a  hunting-  s[)ecies.  In  all  ])rol)- 
ability  llie  wood  duck  will  always  reiuaiu  secondary  to  other  species  of 
watei'fowl  in  Califonua  and  will  need  some  tyjie  of  j)rotection  and 
assistance  to  maintain   its  pi-esent   le\-el. 

While  conii)ilin<i'  the  early  hist()i'\'  of  the  wood  duck,  it  Avas  found 
that  its  status  varied  f>reatiy  according-  to  the  obserx-er.  -lust  how 
nnmerons  the  wood  duck  was  (lurin<>'  the  early  settlenieid  of  California 
is  unknown,  but  it  was  reported  to  be  conunon  and  widespread  from  tlu; 
San  floaquin   \'alley  northward. 

The  wood  dnck  was  fairly  abnndaid  after  iHoO.  Kennerly  (^1851)) 
i-ecorded  the  s])ecies  as  abnndaid  in  the  \icinity  of  San  Francisco  in 
Fel)niar\-  of  isr)4.  Fisher  (1920)  quoted  Belding'  as  reportino'  that 
when  he  moved  to  Mai-ysville  in  1S()2  the  wood  duck  was  very  conunon 
along'  the  Feather  River  and  was  a  continual  resident  in  that  area. 
Mailliard  (1!»11)  reported  that  it  was  conunon  in  Marin  and  Sonoma 
Counties  in  the  ISTO's.  Townseud  (ISST)  stated  that  the  wood  duck 
was  a  conunon  and  comparatively  well  dist  I'ibuted  species  and  it  was 
observed  in  cpiite  large  tlocks  along  the  lower  AlcCloud  Iviver  at  \arious 
times  throughout  the  fall  and  winlei-.  <ii-innell  and  Ui-yant  (lf»14) 
wrote  that  the  wood  diick  was  foi-nierl\-  conunon  and  well  distributed 
throughout  the  lowlands  west  of  the  Sierra  Nevada  Mountains. 

'file  first  game  law  in  California  was  passed  in  IS.l'J  and  protected 
elk,  di'ry,  antelope,  (piail,  mallard  and  wood  duck  for  six  months  of 
the  year.  This  law  ai)plied  to  only  12  counties,  most  of  which  were 
submarginal  habitat  as  far  as  the  wood  duck  was  concerned. 

The  reason  for  this  restriction  on  the  wood  dnck  was  (piite  vagne 
since  at  the  same  time  it  was  considered  to  be  abundant,  'i'his  first 
game  law  did  little  to  |)rotei-t  the  game  s])ecies  it  covered  because  at  the 
time  there  were  no  game  wardens  in  State  employment  to  enforce 
the  legislation.  Apparently'  mai-ket  hunting,  especially  for  the  valuable 
highly  colored  feathers  of  the  male,  bi'onght  about  this  early  restriction. 

1  Subinittecl   for   publication   March,    1960.   A   contribution   of   Federal    Aid    in   Wildlife 
Restoration  Project  W-HO-R,  "Watorfnwi  Investigation." 

(241) 


242  CALIFORNIA   FISH   AND  GAME 

At  tlie  turn  of  tlir  century  tlie  wood  duck  population  was  docliuin"' 
in  numbers.  J)ue  to  tlu'  lack  of  pi'opet'  law  eid'oi-ceinent,  market  hunt- 
in<:-  was  continued.  Di-ainin^  and  reclaimin<i'  uuirsldaiuls  for  ayricul- 
tural  pni'poses  aided  in  llie  decline.  Dredtziiej  for  L;<ild  alon<i'  the  rivers 
was  another  factor  in  the  de<-line.  Hoi  h  land  i-eclamation  and  dred<iin<i' 
destroyed  the  riparian  habitat  frecjuented  by  the  birds.  The  wood  duck 
was  reported  to  be  on  the  verge  of  extinction  by  1914.  Griniiell  (1915) 
reported  that  the  wood  duck  was  then  rather  rare  as  a  resident  in  the 
Sacramento  and  San  Joaqnin  Valleys  and  westwardly  toward  the  coast. 

Destruction  of  liabitat  and  overshooting'  was  the  general  trend 
throughout  the  nation.  The  wood  duck  population  became  depleted  to 
such  an  extent  that  when  Congress  passed  legislation  in  1913  to  protect 
migratory  Avaterfowl,  the  wood  dnck  was  given  complete  ])rotection  for 
five  years.  More  protection  was  given  the  species  when  the  Migratory 
Bird  Treaty  between  the  United  States  and  Great  Britain  was  signed  in 
1918,  devoting  Article  IV  to  the  special  protection  of  the  wood  duck 
and  eider  dnck.  Complete  protection  was  extended  to  the  wood  dnck 
until  1942,  when  one  duck  was  allowed  in  the  hunter's  bag  limit.  Under 
this  protection  the  wood  duck  increased  in  California  as  is  shown  by  a 
report  (Anon.  lil^O)  which  stated  "A  marked  increase  of  wood  ducks 
has  been  noted  in  California  during  the  past  few  years.  This  species 
has  been  protected  by  law  everywhere  since  the  adoption  of  the  Migra- 
tory Bird  Treaty,  and  the  good  results  have  been  apparent  in  many 
parts  of  the  country.  One  warden  rejiorts  a  concentration  of  5,000  wood 
ducks  congregated  on  Lake  Almanor,  Plumas  County,  and  another  con- 
centration is  reported  from  the  Butte  Creek  section,  Butte  and  Sutter 
Counties,  where  several  thousand  wood  ducks  were  said  to  have 
wintered." 

Stoner  (1940)  reported  that  by  1939  wood  ducks  had  increased  in 
abundance  in  favorable  areas  along  creeks  in  Napa  and  Solano  Counties. 

The  protection  given  the  wood  duck  from  hunting  resulted  in  a  gen- 
eral increase,  but  failed  to  return  the  species  to  its  original  numbers 
in  most  places.  More  and  more  land  was  drained  and  reclaimed.  River 
channels  were  straightened,  eliminating  the  wooded  oxbows  frecjuented 
by  the  birds.  Mature  oaks,  sycamores  and  willows,  trees  most  likely  to 
have  nest  cavities  (Fig.  1)  were  cut  and  destroyed.  A  shortage  of 
nest  sites  throughout  California  was  the  result.  This  condition  in 
California  paralleled  a  similar  situation  that  existed  throughout  the 
nation.  It  was  at  this  time  that  the  development  of  artificial  nest 
boxes  occurred.  The  boxes  proved  to  be  successful  in  wood  duck  man- 
agement and  many  thousands  have  been  installed  throughout  the 
nation. 

OBJECTIVES 

The  j)rimary  objective  of  this  survey  was  to  obtain  data  regarding 
the  success  of  a  program  of  nest  box  installation.  The  survey  was 
meant  to  be  a  pilot  studj^,  with  limited  scope,  aimed  toward  presenting 
recommendations  for  use  in  guiding  a  large  scale  nest  box  program, 
in  the  event  such  a  program  proved  feasible  in  California.  A  secondary 
objective  was  the  development  of  an  adequate  method  of  determining 
the  yearly  status  of  the  wood  duck  in  California. 


THE   WOOD   DUCK    IN    CALIFORNIA 


243 


FIGURE    1.      Wood    ducks    do    not    nest    on    the    ground,    instead    they    select    natural    hollows    or 

cavities  in  trees. 


PROCEDURE 

The  following  is  a  list  of  terms  and  definitions  which  have  come  into 
common  nsag'e  dnring  the  study.  This  explanation  may  help  to  clarify 
some  of  the  data  in  this  rejiort. 

Site :  Each  individual  unit  or  area  in  which  nest  boxes  are  located. 
A  site  may  contain  one  or  more  boxes. 

Location  :  The  ti'ee  or  pole  to  which  the  box  is  attached. 

Functional :  Any  box  in  a  condition  to  be  used  by  a  wood  duck  or 
other  animal. 

Nonfunctional :  Any  box  which  was  considered  unsuited  for  wood 
duck  usage.  Some  examjilcs  of  boxes  which  were  considered  nonfunc- 
tional were  those  with  covers  missing,  flooded,  split  badly,  or  concealed 
by  vegetative  growth. 

Wood  Duck  Usage:  AVood  duck  usage  was  considered  to  have  oc- 
curred if  one  or  more  e<iRs  were  laid  in  the  box. 


244 


CALIFORNIA  FISH   AND  GAME 


FIGURE   2.      A   shady    bank    provides    a    loafing    spot    for    the    mole    as    he    waits    for    the    female 
during  the  early  stage  of  incubation.  (Phoiograph  by  F.  Dale  Horn.) 

Percent  T^sa^e:  The  number  of  boxes  used  by  wood  ducks  in  rela- 
tion to  tile  juuiiber  of  functional  boxes  checked. 

Double  Usage :  A  box  in  Avhich  one  female  wood  duck  hatched  off  a 
clutch  with  the  young  leaving  the  box,  and  the  same  box  was  used 
again  during  the  same  season  by  another  female  as  a  nest  site.  These 
boxes  were  recorded  as  two  boxes  used  by  wood  ducks  in  computing 
percent  of  use. 

Successful  Box :  Any  box  from  which  one  or  more  wood  duck  eggs 
hatched  with  ducklings  leaving  the  box. 

Percent  Successful:  The  relationship  between  the  number  of  success- 
ful boxes  and  the  total  number  of  boxes  used  by  wood  ducks. 

Other  Usage:  All  usage  other  than  that  by  wood  ducks  is  included 
in  other  usage.  This  included  boxes  where  there  was  evidence  that  an 
animal  had  entered  the  box  to  den,  roost,  nest  or  seek  food. 

No  Usage :  If  no  evidence  was  found  of  usage  by  wood  ducks  or  other 
animals,  the  box  was  listed  as  unused. 

The  procedure  used  in  installation  of  boxes,  exjilained  in  the  follow- 
ing paragraj)hs,  may  save  others  considerable  experimenting  in  work- 
ing out  satisfactory  methods. 

It  is  impossible  to  li.st  all  areas  where  a  wood  duck  w  ill  locate.  The 
way  to  insure  usage  is  to  install  the  boxes  in  areas  where  the  ducks 
have  been  known  to  nest.  Nest  boxes  are  needed  most  where  the  num- 
ber of  wood  ducks  is  greater  than  the  number  of  nest  sites  available. 


THE   WOOD   DUCK    IN    CALIFORNIA 


245 


FIGURE   3.      Slow    moving    streams    and    small    ponds    subject   to    little    water    fluctuation    provide 
natural  foods  and  cover  for  broods.  (Phoiograph  by  F.  Dale  Horn.) 


FIGURE   4.      Butte    Slough    in    Sutter    County    is    typical    of    streams    and    rivers    in    the    Central 

Valley  inhabited  by  wood  ducks. 


Therefore,  the  first  step  in  placement  of  boxes  is  to  determine  if  wood 
dnelvs  already  inhabit  the  area  in  which  the  boxes  are  to  be  placed. 
Consnlting-  landowners,  sportsmen,  fish  and  game  personnel  working 
in  the  area,  or  aerial  or  ground  reconnaissance  are  usually  good  meth- 


246 


CALIFORNIA   FISH    AND   GAME 


FIGURE   5.      Ideal    habitat    in    Shasta    County.    The    addition    of    nest    boxes    in    areas    such    as 

these  increase  the  production  of  wood  ducks. 

ods  of  discovering  if  wood  ducks  occur  in  a  specific  area  during'  the 
nesting  season. 

The  best  locations  for  boxes  are  in  open  stands  of  trees  along  small 
streams  and  ponds.  Wood  ducks  frequent  the  quiet  waters  of  sloughs, 
old  river  channels,  ponds  and  waterways  where  oaks,  willows  and 
cottonwoods  shade  the  banks  and  furnish  nest  cavities.  An  impor- 
tant need  of  the  wood  duck  is  an  area  adjacent  to  the  nesting  site 
which  provides  resting  and  feeding  cover.  In  most  cases,  the  birds 
prefer  the  smaller  water  areas  to  the  larger  lakes  and  rivers.  Boxes 
should  be  installed  as  close  to  the  water  areas  as  possible.  Generally, 
the  greater  the  distance  a  wood  duck  nests  from  Avater,  the  greater 
the  hazard  faced  by  the  young  in  tlieir  travel  from  the  nest  to  the 
nearest  water.  Figures  2-7  illustrate  various  habitats  utilized  by  the 
wood  duck. 

Since  wood  ducks  do  not  appear  to  be  particularly  adept  at  locat- 
ing nest  cavities,  the  boxes  should  be  placed  in  areas  where  they 
can  be  seen  easily  by  the  ducks.  All  vegetation  which  conceals  the 
box  should  be  cut  away  at  the  time  the  box  is  installed. 

The  height  of  the  box  above  the  ground  was  not  considered  too 
important  as  long  as  it  was  higher  than  10  feet.  Boxes  placed  above 
10  feet  in  trees  which  were  devoid  of  limbs  below  the  boxes  proved 
to  have  less  molestation  and  human  interference.  Such  a  situation, 
however,  required  a  ladder  or  climbers  and  safety  belt  for  the  person 
checking  the  box  for  usage. 


THE   WOOD  DUCK   IN    CALIFORNIA 


247 


FIGURE   6.      Dredger    ponds    occur    along    the    western    slope    of    the    Sierra    foothills    but    many 
lack    nest   cavities,   which    makes    these    ponds    ideal    for   the    installation    of    nest   boxes. 


FIGURE   7.      This    small     pond     in    Marin     County    was    considered     ideal     habitat     lacking     only 
nest  cavities.  Two  pair  of  wood  ducks   moved   in  and   nested   immediately  after  the   installation 


,*  ♦,. 


:i4c^ 


CAI.iFOKXIA    I'MSII    AND    (JAM 


X  I  1/4   Cleats 


Top  (inside) 


T~  '■ 

4"  Shavings 
.1 


10" 


1^ 


Front 


J 


II     — — .n 


25     22 


TT 

1 


^-Drilled  hole  7/16" 


r 


Side 


Materials 


l"x  12"  rough  lumber 
3/8"x  3  1/2"  hanger  bolt 
3/8"  wing  nut  end  washer 

2"  screen  door  hooks  and  eyes 
shavings  as  shown 

FIGURE    8.      Plan    of    wood    duck    nest    box.    The    elliptical    entrance    usually    eliminates    pilfering 
of  the  nest  by  racoons.  (Drawn  by  Cliffa  Corson.) 

The  boxes  used  were  patterned  after  the  U.S.  Fish  and  Wildlife 
Service  design.  Two  sizes  were  nsed  during  the  study.  One  size  was 
12  inches  square  and  24  inches  long  and  the  other  was  10  inches  square 
and  22  inches  long  (Figure  8).  There  was  no  definite  preference  shown 
by.  the  wood  ducks  for  either  size  of  box.  By  utilizing  the  smaller 
boxes,  the  cost  of  materials  was  reduced. 


THE   WOOD   DUCK   IN    CALIFORNIA  249 

The  boxes  were  coiistrneted  of  one-inch  ron«'h  redwood  IuihIxm-.  The 
rough  surface  of  the  lumber  was  an  aid  to  the  young  in  climbing  out 
of  the  box.  Redwood  Avas  selected  because  of  its  resistance  to  weather 
and  rotting,  and  because  it  was  as  cheap  or  cheaper  than  rough  pine 
or  fir.  However,  it  was  more  suscojitible  to  s])litting. 

The  cost  per  unit  at  the  time  of  construction  during  this  study  was 
$1.05  for  the  22-inch  and  $1.24  for  the  24-inch  boxes.  This  cost  in- 
cluded the  hanger  bolt  and  hardware,  but  not  labor.  The  cost  could 
be  reduced  by  buying  the  material  in  larger  lots. 

The  box  was  attached  to  the  tree  by  a  hanger  bolt.  The  box  was 
hung  on  the  bolt  through  the  hole  bored  in  the  back.  The  wingnut 
and  washer  drew  it  tightly  to  the  tree.  The  wingnut  could  be  loosened 
to  relieve  pressure^  as  the  tree  grew.  This  method  of  attachment  proved 
successful  and  simi)lified  installation  for  the  installer.  The  nesting- 
box  should  be  firm  and  any  movement  kept  to  a  minimum.  A  iiail 
through  the  lower  tAvo  inch(\s  of  the  back  of  the  box  was  used  to  steady 
it,  if  needed.  Boxes  hanging  loosely  were  Tisually  rejected  by  the  female. 

Potential  nest  box  sites  were  evaluated  with  regard  to  their  suit- 
ability as  wood  duck  habitat.  The  factors  considered  were  available 
food,  nest  cover,  cover  for  broods,  loafing  cover  and  gencn-al  water- 
fowl usage.  Most  of  the  boxes  were  installed  during  the  late  winter,  a 
practice  which  enabled  the  crew  to  place  the  boxes  above  flood  or  high 
water  levels;  however,  it  necessitated  evaluating  some  of  the  above 
factors,  such  as  food  and  brood  cover,  at  the  time  of  the  first  box 
check  in  the  spring. 

A  box  of  sound  construction,  securely  fastened  to  a  tree  or  pole  in 
a  suitable  location,  Avere  important  factors.  The  joersonnel  checking 
the  boxes,  by  noting  the  areas  and  factors  of  maximum  success,  gained 
experience  of  great  value  for  use  in  the  erection  of  additional  boxes. 
This  experience  can  eliminate  wasted  effort  resulting  from  too  many 
boxes  placed  in  unsuitable  sites.  Better  success  Avill  result  if  the  men 
engaged  in  the  program  are  familiar  with  the  wood  duck's  preferences 
for  nesting  sites. 

When  a  box  Avas  installed,  a  field  data  sh(;et  Avas  filled  out  recording 
general  location,  installation  site,  method  of  installation  and  rating  of 
the  area  as  Avood  duck  habitat.  Such  data  as  tree  species,  height  of 
box,  and  direction  of  hole  Avere  recorded  and  proved  valuable  as  an 
aid  in  relocating  boxes  Avhich  were  difficult  to  find.  A  map  of  the  box 
location  Avas  draAvn  at  the  time  and  any  useful  information  Avas  put 
on  the  map.  The  maps  Avere  redraAvn  latei-  and  added  to  a  permanent 
file  to  be  used  during  subsecpient  box  checks.  Each  box  Avas  numbered 
to  aid  in  collection  of  data  for  the  individual  nest  box  history.  The 
boxes  also  Avere  stenciled  Avith  information  designed  to  forestall  any 
human  molestation  resulting  from  curiosity  or  A^andalism  (Figure  9). 

All  boxes  Avere  checked  tAvice  during  the  season.  The  first  inspection 
Avas  in  early  May  and  coincided  for  the  most  part  Avith  the  peak  of 
the  nesting  season.  The  nesting  season  Avas  slightly  earlier  in  the  south- 
ern parts  of  the  range,  a  condition  which  allowed  the  personnel  check- 
ing the  boxes  more  time  to  iiisjx'ct  all  th(>  boxes. 


'2:)0 


CALIFOKNIA    FISH    AM)   (!AMK 


l'''^;^"''-*' 


'l;'j^ 


J,3'4^a  ii^K'^Ldf. 


FIGURE   9.      Wood    duck    nest    box    showing    box    number    and    stencilled    information    designed 

to  keep  human  molestation  at  a  minimum. 


The  second  check  was  made  in  July  at  which  time  the  nesting  season 
was  considered  complete.  Few,  if  any,  nests  were  active  after  July. 
The  field  work  was  considered  complete  when  the  last  check  was 
finished. 

During  the  first  check,  a  nest  card,  of  the  Unisort  Analysis  type, 
was  made  out  for  each  box  and  pertinent  data  recorded  on  the  card. 
The  same  card  was  used  also  on  the  second  check.  A  functional  box 
was  checked  to  determine  usage.  The  boxes  which  were  nonfunctional 
were  repaired  or  replaced. 

The  nests  were  examined  to  determine  the  number  of  eggs  present 
and  whether  they  were  being  incubated.  The  amount  of  down  present 
was  recorded,  as  this  usually  gave  an  indication  of  the  stage  of  in- 
cubation. 


THE   WOOD   DUCK   IN    CALIFORNIA  251 

Successful  nests  were  examined  to  determine  the  size  of  the  hatch, 
the  number  of  eggs  remaining  and  the  number  of  dead  ducklings  left 
in  the  box.  The  iiumber  of  eggs  hatched  was  determined  by  examina- 
tion of  the  remains  and  counting  the  egg  membranes  which  remain 
intact  even  though  the  shells  are  crushed. 

Unsuccessful  nests  were  examined  to  determine  the  reason  for  their 
failure  and  to  ascertain  the  number  of  eggs  lost,  if  any.  Eggs  left  in 
the  boxes  were  broken  to  determine  if  incubation  had  progressed 
enough  to  be  apparent.  Desertion  was  assumed  where  no  eggs  hatched 
and  no  definite  evidence  of  interference  was  observed. 

Other  usage  was  recorded  by  species  and  the  nature  of  usage.  Some 
boxes  might  have  been  used  for  nesting  or  denning,  some  for  roost- 
ing, while  others  might  have  been  visited  by  an  animal  in  search  of 
prey. 

All  boxes  with  usage  data  completed  were  cleaned  of  egg  remains, 
down  and  feathers  to  prevent  confusion  in  the  next  year's  data.  New 
Avood  shavings  were  added  where  needed  to  maintain  a  level  of  about 
four  inches  in  the  box.  Shavings  were  preferred  over  sawdust,  since 
the  sawdu.st  tended  to  pack  and  become  hard.  A  hard  packed  surface 
would  not  allow  the  eggs  to  be  buried  during  the  laying  period  and 
might  have  resulted  in  the  female  abandoning  the  box  as  a  nest  site. 

WOOD   DUCK   HABITAT  IN   CALIFORNIA 
Summer  Habitat  and  Population 

The  greatest  population  of  breeding  wood  ducks  in  the  United  States 
is  found  in  the  states  from  the  upper  Mississijipi  River  eastward 
through  New  England.  Ideal  habitat,  such  as  small  wooded  ponds, 
bogs,  flooded  swamps  and  slow  moving  streams,  is  interspersed  through- 
out this  area. 

In  California,  the  summer  wood  duck  population  is  distributed 
sparsely  over  most  of  the  state  north  of  the  Tehachapi  Mountains. 
Their  range  includes  a  tremendous  amount  of  marginal  habitat.  Much 
of  this  habitat  consists  of  streams,  rivers  and  reservoirs,  ranging  from 
the  higher  elevations  to  the  river  bottomlands  in  the  valleys.  Wood 
ducks  were  observed  throughout  this  habitat  wherever  any  effort  was 
expended  on  box  installation.  There  were  53  sites  in  the  State  where 
nest  boxes  were  installed,  and  wood  dncks  utilized  boxes  in  46  of 
the  sites. 

There  are,  however,  some  areas  of  concentrations.  These  are  located 
as  follows:  an  area  east  of  Anderson,  Shasta  County,  which  includes 
many  wooded  streams  and  the  Sacramento  Kiver ;  Indian  Valley  in 
Plumas  County;  along  the  Feather  River  in  Butte,  Sutter  and  Yuba 
counties;  the  Butte  Sink  west  of  Gridley,  Butte  County;  soutli  along 
the  western  slope  of  the  Sierras,  including  stretches  of  the  Cosumnes, 
Mokelumne,  Tuolumne,  Merced,  San  Joaquin  and  Kings  rivers.  Most 
of  the  north  coastal  streams  also  are  utilized  by  some  breediiig  pairs. 
These  areas  mentioned  are  by  no  means  a  complete  list  of  concentra- 
tions of  breeding  wood  ducks  in  California.  Other  areas  undoubtedly 
exi.st  which  were  not  located  during  the  study. 

Most  of  the  available  habitat  in  California  is  subjected  to  extreme 
fluctuations  of  water  levels.  This  condition  has  a  detrimental  effect  on 
most  wildlife  including  the  wood  duck.  Unstable  water  conditions  may 


2.')"2  CALTFORXIA   FISTI    AXD    r!A:\rE 

])lay  ail  iinportaiit  jiai'l  in  limit  ini;-  the  iiuiiibcr  of  wood  ducks  breed- 
ing in  the  State.  The  niajoi-  rainfall  in  California  comes  dnrino-  the 
M-inter  months  and  the  How  in  most  streams  is  ])lentifnl  at  that  time. 
liy  late  spring'  the  runoff  from  tlie  snow  paclv  is  under  way,  but  much 
of  this  is  divertt'il  for  agricultural  |)iiri)oses.  The  result  is  a  decrease 
of  water  in  streams  until  the  flow  in  early  summer  is  reduced  to  a 
minimum  or  stopped  altogether.  This  decrease  in  available  water  co- 
inciiles  with  the  nesting  season  of  the  wood  duck.  The  rapid  decrease 
of  water  and  the  lack  of  natural  nest  cavities  apparently  are  the 
imi)ortant  factors  in  making  California  habitat  marginal.  The  fact  that 
California  is  the  southern  extremity  of  the  breeding  range  on  the 
Pacitic  Coast  also  contributes  to  the  limited  breeding  populations  within 

the  State. 

As  a  result  of  field  observations  during  the  five-year  study,  the 
annual  nesting  wood  duck  population  in  California  was  estimated  at 
1,5UU  i)airs. 

The  estimated  breeding  range  of  the  Avood  duck  in  California  is 
shown  in  Figure  10. 

Winter  Habitat  and  Population 

California  is  the  major  wintering  area  for  the  wood  duck  on  the 
Pacific  Coast.  A  few  stragglers  are  seen  in  Nevada  and  Arizona  and 
some  winter  in  Sinaloa,  in  Central  Mexico  (A.O.U.  Checklist,  5th 
Edition). 

There  are  more  than  25,000  miles  of  streams  and  about  6,000  lakes 
and  impoundments  in  California  and  many  of  those  of  lower  elevation 
are  utilized  by  wood  ducks  during  the  winter.  Wood  ducks  have  been 
recorded  in  the  fall  and  winter  from  San  Diego  County,  Imperial 
Valley,  and  Death  Valley  in  the  south  to  Humboldt  and  Siskiyou 
counties  in  the  north.  They  have  been  reported  in  Santa  Barbara, 
Ventura,  and  Mendocino  counties  on  the  coast  and  east  to  Yosemite 
National  Park  and  Lake  Tahoe  in  the  Sierra  Nevada  Mountains.  Cen- 
tral California,  however,  furnishes  most  of  the  winter  habitat.  Oak- 
covered  foothills  bordering  the  central  valleys,  the  rice  belt,  and  the 
river  bottomlands  are  all  adjacent  to  each  other  and,  when  combined 
Avith  the  warm  winters  and  abundant  I'ainfall,  form  an  ideal  winter 
habitat. 

Although  the  wood  duck  is  widely  dispersed  throughout  the  winter- 
ing range,  there  are  areas  of  concentration.  These  areas  correspond 
closely  to  the  summei-  concentrations  and  may  be  found  as  follows: 
east  of  Anderson  in  Shasta  County;  in  the  vicinity  of  the  confluence 
of  Deer  Creek  and  the  Sacramento  River  in  Tehama  County ;  along  the 
Feather  River  in  Butte,  Sutter  and  Yuba  counties;  the  Butte  Sink 
west  of  Gridley,  Butte  County;  in  the  foothills  of  the  Sierra  Nevada 
IMountains,  including  the  many  rivers  and  streams  draining  into  the 
central  valleys  as  far  south  as  the  Kings  River ;  and  on  the  many  reser- 
voirs and  streams  along  the  Coast  and  Diablo  ranges,  south  to  Mon- 
terey County.  The  wood  duck  is  rarely  found  along  the  sea  coast  or 
in  the  salt  marshes. 

The  winter  migration  of  the  resident  po])ulation  in  California 
amounts  to  a  shift  out  of  the  higher  elevations  into  the  central  valleys 
and   adjoining   foothills.   The   central   valley   is   apparently  the  year- 


THE   WOOD   DUCK    IN    CALIFORNIA 


253 


FIGURE    10.      Estimated    summer    (breeding)   and    winter   range   of  the   wood    duck    in    California. 
The  shaded  portions  of  the  map  indicate  areas  of  higher  densities  of  wood  ducks. 

(Drown   by  Cliffa  Corson.) 


roiuid  range  of  the  wood  chieks  that  breed  tliere.  The  iiiai)  in  Figure  lU 
illustrates  the  estimated  winter  range  in  California. 

Most  of  the  wood  ducks  in  llie  Pacific  Fly  way  are  ]>  rod  need  in 
Washington,  Oregon  and  California,  with  linnted  i)o|)nlations  in  west- 
ern Montana,  northern  Idaho  and  the  Cohuubia  IJasin  in  British 
Columbia.  Recoveries  of  birds  banded  by  those  states  indicate  a  fall 
migration  into  tlie  wintering  areas  of  California.  The  recovery  pattern 
for  banded  wood  ducks  taken  in  California  is  shown  in  Figure  11.  As 
seen  from  the  map,  tlie  Coast  Ranges  north  of  San  Francisco  liny,  the 
Sacramento  Valley  and  the  northern  San  Joaquin  Valley  are  important 
wintering  areas  on  the  Pacific  Coast. 


•_':)4 


CAMFOKMA    I'MSIl    AND    CA.MK 


DEER  ISLAND 


LAKE   TERRELL- 
SKAGIT  DELTA 


Q  NINEPIPE  N.W.R. 


_  SAUVIE   ISLAND 
j^#    SMITH  LAKE 

•  WILLOW  LAKE 

E   E    WILSON   G.  M.  A. 


ACRESCENT  MILLS 


••• 


At. 


FIGURE    11.      Migration   of  banded   wood   ducks  info  California.   The   large   symbol   indicates  the 
banding  station  and  the  small  symbol  represents  the  area   of  return.   (Drawn  by  C/iffa   Conon.) 


The  extensive  habitat  in  California,  coupled  with  the  secretive  nature 
of  the  species,  makes  it  very  difficult  to  obtain  an  accurate  census  of 
the  total  population.  In  trying  to  resolve  the  question  of  how  many 
wood  ducks  winter  in  the  State,  an  indirect  method  was  thought  to  be 
best.  In  this  way,  by  determining  the  total  fall  population  in  those  states 
where  California's  wintering  wood  ducks  originate,  the  California  pop- 


I 


THE   WOOD   DUCK    IN    CALIFORNIA 


255 


Illation  conld  be  calculated.  Tabic  1  presents  the  estimates  by  water- 
fowl technicians  of  the  ])reniijiratioii  ])()|)iilations  wiHiiii  their  states 
during  1958.  It  should  be  kept  in  mind  that  the  wood  duck  does  not 
lend  itself  to  easy  census  and  therefore  the  figures  in  the  table  are 
obtained  under  less  than   i(h'al  conditions  and  mav  be  subject  to  ci'i'or. 


TABLE  1 
Fall  Populations  of  Wood  Ducks  in  the  Pacific  Flyway,  1958 


Area 

Estimated 
breeding  pairs 

Estimated 
total  fall  pojjulation'- 

Britisli  Columbia.  _  . 

Washington 

200 

30,000 

100 

560 

■•7,500 

1,500 

1,000 

37,000 

500 

Northern  Idaho 

3,300 
35,000 

California 

7,200 

Total 

15,860 

84,000 

1  Arizona  and  Nevada  are  not  included. 

-  Where   only   pairs   were   given,    the   total    fall    |jii|)iilatiiin   was   computed    with   averane    figures    of    70    iieicent 

nesting  success  and  four'  young  |)er  hrood  fledged. 
■'  Number  of  bleeding  pairs  not  given,  but  an  estimated  33  percent  were  adults. 
'  .Nesting  success  at  fiG  percent,  or  5,000  successful  pairs,  and  4  young  per  l)niod  fli'dged. 


As  shown  in  Tal)l('  1,  a])proximately  84,000  wood  ducks  were  present 
in  the  tlyway  at  the  beginning  of  the  1!)58  hunting  season.  The  esti- 
mated number  of  wood  ducks  killed  in  the  Pacific  l^Tj^way  during  the 
1958-59  waterfowl  season  was  over  22,400  birds  (Crissey,  1959).  This 
estimattMl  kill  subtracted  from  the  total  tlyway  population  left  a  post 
hunting  season  population  of  about  61,600  wood  ducks  in  the  flyway. 
It  was  estimated  that  at  least  90  percent  of  the  flyway  population,  or 
about  55,400  wood  ducks,  wintered  in  California.  The  above  data  are 
admittedly  rough  and  unrefiiKMl  but  they  do  give  a  better  picture  of 
the  wood  duck's  status  in  California  as  it  exists  at  the  present. 

There  is  a  definite  need  for  a  reliable  method  of  censusing  wood 
ducks,  both  in  the  summer  and  winter.  One  of  the  objectives  of  this 
study  was  to  devise  a  census  method  in  California,  but  very  little  in- 
formation was  obtained. 

Various  census  methods,  including  aerial  surveys,  stream  surveys, 
and  brood  counts  have  been  tried  by  other  states,  with  varying  degrees 
of  success.  One  of  the  latest  methods,  now  being  tried  in  other  states, 
is  an  evening  count  at  known  roosting  locations.  This  method  appears 
to  hold  some  promise  for  more  efficiency  in  measuring  the  trend  of  wood 
duck  pojjulations.  A  report  on  wood  duck  research  methods  (Massa- 
chusetts Division  of  Fisheries  and  Game,  undated)  states:  "An  overall 
census  of  waterfowl  populations,  however,  may  be  open  to  wide  mis- 
interpretation since  the  degree  to  which  any  individual  species  can  be 
censused  may  vary  greatly.  Wood  ducks  in  jiarticular  are  difficult  to 
census  at  this  season.  Often  the  woodies  form  in  bands  which  frccpient 
areas  different  from  those  occupied  during  the  summer  months.  Usually 
these  areas  are  swamps,  wooded  streams,  and  small  areas  difficult  to 
census  by  ordinary  methods.  Perhaps  the  best  census  of  wood  ducks 
at  this  season  can  be  obtained  by  evening  flights  at  known  concentration 


2r)6 


LAl.IFORXTA    FTSTT    AXO    nA^tlE 


points.  Ill  \ic\v  of  llic  uiJiiiy  vai'\iii^-  influciu'cs  which  must  effect  the 
eeiisusiiiy-  of  a  wood  duck  po])ulati()ii  it  would  scciu  that  more  iiiforma- 
tiou  cau  be  <>athered  from  intensive  stndy  on  a  few  areas  than  by  an 
extensive  but  su|)erficial  count  on  many  areas.  This  is  evi(h'nt  at  h^ast 
unlil  such  lime  as  cciisiis  techiiifines  |)rove(l  by  intensive  study  cau  be 
(U'velojx'd  and  ap|)lied  on  an  extensive  basis." 

LOCATION   OF   NEST   BOXES 

Tlie  nest  box  i)rogTam  was  started  iu  California  in  1952  on  a 
very  limited  scale,  with  only  eleven  boxes  bein^'  erected  during  the  year. 
The  project  was  expanded  to  47  boxes  during  1953  and  to  145  boxes  in 
1954.  The  number  of  boxes  available  fluctuated  considerably  each  year, 
due  to  loss  by  destruction  and  to  the  relocation  of  some  boxes  on  better 
sites.  Attention  was  given  lu-imarily  to  a  waterway  or  an  area  consid- 
ered to  be  good  habitat.  The  region  and  county  in  which  it  was  located 
was  of  little  significance.  The  number  of  boxes  in  the  various  counties 
is  shown  in  Table  2. 

TABLE  2 
Location  and  Number  of  Wood  Duck  Nest  Boxes  Installed  1952-1956 


Region 

County 

Number 

Region 

County 

Number 

Region 

County 

Number 

I 

Shasta 

Humboldt- - 

Modoc 

Lassen 

Tehama 

Total 

13 

12 

4 

3 

3 

II 

Plumas 

Yuba 

Colusa 

Sacramento 

Sutter 

Yolo 

Butte 

Total 

19 
16 
11 
6 
5 
5 
4 

III 
IV 

Lake 

Marin 

Mendocino 

Total 

Merced 

Fresno 

Total 

6 
5 
2 

13 

23 
15 

3.5 

66 

38 

All  Hcsions  sniiul  total 152 


As  illustrated  in  Figure  12,  most  of  the  major  river  drainages  were 
sampled.  For  the  most  part,  wood  duck  habitat  in  California  is  associ- 
ated with  the  streams  and  rivers.  Small  permanent  ponds  and  bogs  do 
not  exist  in  any  number.  AVhere  small  ]ionds  and  water  areas  did  exist, 
an  effort  was  made  to  erect  boxes  on  those  sites,  ^lore  work  should  have 
been  done  on  the  many  dredger  ponds  along  the  western  slope  of  the 
Sierra  Nevada  Mountains.  The  number  of  boxes  installed  and  the  areas 
covered  were  consider(Hl  sufficient  to  ]~iermit  an  evaluation  of  the 
program. 

NEST   BOX   UTILIZATION 

Wood  Duck  Usage 
Percent  of  Boxes  Used 

It  may  be  determined  from  Table  3  that  an  average  of  42  percent  of 
the  boxes  were  used  by  wood  ducks.  Usage  of  the  boxes  by  other 
wildlife  w^as  recorded  in  31  percent  of  the  functional  boxes.  There  w^as 
no  activitj'  recorded  in  31  percent  of  the  boxes. 


THE   WOOD   DUCK    IN    CALIFORNIA 


257 


•■^^o-c-^Q 


FIGURE    12.      Wood    duck    nest    box    sites    in    California.    Each    dot    indicates    one    or    more    nest 
boxes  installed  in  the  area.  (Drawn  by  Clifia  Corson.) 


The  degree  of  usage  by  wood  ducks  varied  greatly  througliout  the 
different  areas  in  the  State.  The  boxes  filled  a  vital  need  in  areas  where 
natural  cavities  were  lacking,  while  in  other  arenas  of  equal  appearance 
oidy  limited  use  occurred.  In  areas  of  limited  tiest  box  use,  it  was 
assumed  that  the  number  of  natural  cavities  was  sut^cient,  that  there 
was  a  small  population  of  wood  ducks  present,  or  that  some  other  fac- 
tors influenced  th(>  nesting.  Figure  18  illustrates  typical  wood  duck 
usage. 

Nesting  Period 

The  beginning  of  the  nesting  season  in  California  depended  upon  the 
particular  area  under  consideration.  The  nesting  cycle  usually  began 
earlier  in  the  southern  part  of  the  range  and  was  progressively  later 


27)8 


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THE   WOOD   DUCK    IN    CALIFORNIA 


259 


FIGURE    13.      A    nest    box    used    by    a    wood    duck.     Note    the    abundance    of    down    which    is 

typical  of  wood  duck  nests. 


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THE   WOOD   DUCK    IN    CALIFORNIA  261 

to  the  north.  Average  dates  taken  from  known  nesting-  pcM'iods  in  wood 
dnek  boxes  indicated  egg  laying  started  about  the  last  Aveek  of  Alareli 
ill  tlie  Sail  -loaquin  Valley  and  during  the  second  week  of  April  in 
Pliuuas  and  Ihnnboldt  counties.  In  general,  the  nesting  season  was  usu- 
ally in  progress  throughont  the  State  after  the  middle  of  April.  Nesting 
activity  progressed  at  a  more  liesurely  pace  in  the  soutlun-n  portion  of 
the  range.  Most  of  the  nesting  activity  was  eom])lete(l  by  -Inly  15  ex- 
cept for  an  occasional  late  nest  or  a  reuesting  attempt. 

Nesting  Success 

A  nest  was  considered  successful  if  one  or  more  ducklings  were 
known  to  have  departed  from  the  box.  Only  in  one  instance  did  all 
young  fail  to  leave  the  box  after  hatching.  In  every  successful  nest, 
the  characteristic  egg  membranes  and  caps  were  found  in  llie  box.  The 
presence  of  these  remains  was  Ihe  criteria  used  in  deteriniiiinu  llie 
fate  of  the  nest. 

During  the  five-year  period,  ii(>st  history  data  were  recorded  on 
164  wood  duck  nests.  Of  these,  125  nests  (76  percent)  were  successfully 
hatched,  16  (10  percent)  were  deserted,  13  (8  percent)  were  destroyed 
and  10  (6  percent)  were  recorded  as  dump  nests.  Table  4  summarizes 
all  data  gathered  of  the  fate  of  nests  throughout  the  study. 

Cluich  Size 

Clutch  sizes  ranged  from  a  iiesi  containing  one  egg  to  ;i  diiiiip  nest  of 
43  eggs.  Successful  clutch  sizes  ranged  from  3  eggs  to  28  eggs  and  tlie 
average,  based  on  125  successful  nests,  was  13.3  eggs  per  nest  (Figure 
14).  However,  this  average  clutch  size  was  considered  to  be  biased  by 
the  influenee  of  parasitism  of  nests  by  other  females.  Nests  containing 
10  to  14  eggs  made  up  52  percent  of  tlie  successful  nests  and  represented 
those  nests  in  which  a  minimum  of  parasitism  had  occurred.  The  aver- 
age clutch  size  of  tliis  group  of  nests  was  11.8  eggs  and  was  considered 
to  be  a  more  valid  figure  for  wood  ducks. 

A  dump  nest  was  defined  as  the  product  of  more  than  one  female 
and  no  attempt  was  made  to  incubate  the  eggs.  A  total  of  10  dump 
nests  were  recorded  during  tlie  study  which  contained  285  eggs.  The 
average  clutch  size  for  dump  nests  was  28.5  eggs  per  nest.  The  dump 
nests  and  large  clutch  sizes  of  successful  nests  indicated  that  there  was 
c()nsidera])]e  competition  among  the  females  foi-  nesting  sites.  Addi- 
tional boxes  installed  in  the  areas  of  competition  would  have  helped 
to  alleviate  this  condition. 

Hatching  Success  and  Production 

Successful  nests  contained  a  total  of  1,663  eggs,  of  which  1,2!)5  or 
78  percent  hatched.  The  young  experienced  little  difficulty  in  leaving 
the  boxes  after  hatching.  A  total  of  1,253  (97  percent)  ducklings 
scrambled  out  of  the  boxes  during  the  study.  Data  obtained  on  nest 
box  utilization  by  wood  ducks  is  summarized  in  Table  5. 

Unsuccessful  Nests 

Unsuccessful  nests  Avere  recorded  ;is  deserted  or  destroyed.  Dump 
nests  were  included  in  this  category  for  lack  of  a  better  place.  A  total 
of  39  nests  (24  percent)  were  classified  as  unsuccessful  during  the 
study. 


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THE   WOOD   DU(!K    IN    CALIFORNIA 


203 


TABLE  5 
Summary  of  Wood  Duck  Nest  Box  Data 


Total  wood  duck  nests 

Total  eggs,  all  nests 

Average  clutch,  all  nests 

Successful  nests 

Total  eggs,  successful  nests 

Average  clutch,  successfvil  nests  _ 

Total  eggs  hatched  „ . 

Average  hatch  in  successful  nests 

Total  young  produced 

Total  young  leaving  boxes 

Average  young  leaving  eacli  box. 
Percent  of  young  leaving  boxes.  _ 


1952 


4 
61 
1.5.3 

2 
24 
12.0 
24 
12 
24 
24 
12 
100 


1953 


18 
265 

14.7 

11 
154 

14.0 
122 

11.1 
122 
118 

10.7 

97 


19.54 


38 
483 

12.7 

31 
438 

14.1 
344 

11.1 
344 
.335 

10.8 

97 


19.55 


50 
644 

12.9 

42 
516 

12.3 
438 

10.0 
438 
422 

10.0 

96 


19.56 


54 
764 

14.1 

39 
.531 

13.6 
367 

9.0 
367 
3.54 
9.0 

96 


Total 


164 
2,217 

13.5 
125 
1,663 

13,3 
1,295 

10.4 
1,295 
1,2.53 

10.0 

97 


Desertion  was  recorded  in  16  (10  percent)  nests.  Desertion  was 
assnined  where  no  definite  evidence  of  interference  was  observed.  The 
causes  of  desertion  are  very  difficnlt  to  determine.  Competition  among 
females  for  nesting  sites,  hnman  interference  and  competition  with 
other  species  of  wildlife  for  nse  of  boxes  were  considered  to  be  causes 
of  desertion. 

There  were  13  nests  (8  percent)  destroyed.  The  main  factor  causing 
nest  destruction  was  attributed  to  human  molestation.  Human  moles- 
Uition  accounted  for  a  total  of  eight  nests  that  were  broken  up  by  the 
removal  of  eggs  or  destruction  of  boxes  containing  nests.  Raccoon 
j)redation,  which  is  prevalent  in  nest  box  ])rograms  in  eastern  states, 
was  found  in  onl}^  two  boxes  and  suspected  in  two  more  during  this 
study. 

8ix  ])ercent  (10  nests)  of  the  boxes  used  by  wood  ducks  contained 
dump  nests. 

Other  Usage 

In  addition  to  usage  by  w'ood  ducks,  the  boxes  provide  nesting  and 
resting  sites  for  many  other  species  of  wildlife.  The  other  species  were 
considered  a  nuisance  as  far  as  the  wood  duck  nest  box  program 
was  concerned.  A  total  of  119  boxes  (31  percent)  was  occupied  by  12 
species  other  than  wood  ducks.  Those  most  commonly  found  using  the 
boxes  were  sparrow  hawks,  honey  bees  and  screech  owls.  Table  (i  pre- 
sents a  list  of  wildlife,  other  than  wood  ducks,  utilizing  the  boxes  dur- 
ing the  study. 

Nonfunctional  Boxes 

A  box  was  considered  nonfunctional  w^hen  there  was  a  condition 
present  to  impede  usage.  Such  conditions  included  tops  missing  from 
boxes,  absence  of  shavings  in  box,  large  splits  in  box  sides,  box  con- 
cealed by  vegetation,  boxes  which  had  fallen  down,  boxes  flooded  by 
high  water,  and  some  types  of  human  molestation  such  as  shooting 
boxes. 

A  total  of  450  boxes  was  checked  during  the  study  and  51  (11  per- 
cent) were  found  to  be  nonfunctional.  As  the  boxes  became  older  the 


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TABLE  6 
Number  of  Boxes  Used  by  Other  Wildlife 


olJccies 


Number  of  boxes 

Percent 

27 

22 

23 

19 

21 

18 

11 

9 

8 

7 

8 

7 

6 

5 

5 

4 

4 

3 

3 

3 

2 

2 

1 

1 

119 

100 

Sparrow  lunvk 

Honey  bees 

Screech  owl 

Red-sliaftod  flicker.. 

Kinstuiled  cat 

Tree  swallow 

Brown  rat 

Barn  owl 

Bird  (unknown) 

Wren 

English  sparrow 

Mammal  (unknown) 

TotaL 


number  that  Avere  iioiifvinctional  increased  proportionately  (Figure 
15).  As  a  resnlt  of  flood  conditions  throngliout  California  during  the 
winter  of  1955-56,  the  number  of  nonfunctional  boxes  nearly  doubled. 
Many  of  the  trees  containing  nest  boxes  were  knocked  down  by  the 
flooding  streams  and  rivers. 

MAINTENANCE 

Tlie  number  of  boxes  successfully  used  by  wood  ducks  each  year 
ultimately  determines  the  value  of  the  program.  Sucli  a  program  can- 
not rest  with  the  initial  installation  of  the  boxes  but  must  have  mainte- 
nance that  is  both  adequate  and  continuing.  In  a  successful  program, 
boxes  must  be  in  a  condition  acceptable  to  the  birds  at  the  beginning 
of  each  nesting  season. 

It  was  found  that  soundly  constructed  boxes  of  good  lumber  resisted 
deterioration  for  long  periods.  However,  when  wooden  boxes  are  used, 
maintenance  and  upkeep  become  a  part  of  the  program.  Boxes  that 
were  destroyed  by  flooding,  vandalism  and  irreparable  splitting  had 
to  be  replaced.  The  replacement  of  destroyed  boxes  Avas  carried  out 
at  the  time  of  the  nesting  checks  during  the  summer.  Nonfunctional 
boxes  Avere  repaired  AA'hen  found.  The  major  cause  of  nonfunctional 
boxes  Avas  the  occurrence  of  large  splits  in  the  sides  beloAv  the  entrance 
hole.  In  most  cases,  such  boxes  were  not  accepted  by  female  Avood 
ducks  as  nesting  sites.  Black  weather  stripping  cement  Avas  squeezed 
into  the  split,  which  Avas  then  closed  AAdth  a  feA\^  corrugated  fasteners. 
This  method  proved  to  be  successful  and  little  time  AA'as  required  to 
repair  a  box  in  this  manner. 

Extra  lids  AA'ere  carried  at  all  times  and  AA'ere  used  as  replacements 
AA'here  needed.  Shavings  Avere  often  removed  from  a  box  by  other  Avild- 
life  and  it  became  standard  procedure  to  have  extra  shavings  along 
AA^ien  checking  the  boxes  for  usage.  In  some  areas,  especially  the  north 
coast,  the  boxes  were  concealed  by  rapid  vegetative  groAvth  after  their 
installation.  This  ncAV  cover  needed  chopping  away  each  year  (Fig- 
ure 16).. 


THE   WOOD   DUCK    IN    CALIFORNIA 


265 


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FIGURE    15.      The    percentage    of    nonfunctional    boxes    in    relationship    to    the    length    of    time 
that  the  boxes  were  installed.  (Drawn  by  Cliffa  Corson.) 


During  the  early  part  of  the  study,  considerable  trouble  was  caused 
by  honey  bees.  They  took  over  nest  boxes  and  used  them  as  hives. 
Tlie  boxes  containinji'  bee  hives  were  poisoned  with  cyanide  during-  the 
winter  when  the  colony  of  bees  was  dormant.   The  boxes  were  then 


266 


CALIFORNIA    FISH    AND  GAME 


FIGURE    16.      This    box    in    Humboldt    County    was    concealed    by    vegetative    growth    and    was 

considered  nonfunctional. 


cleaned  out  and  replaced.  Some  experimenting  was  done  witli  repellents 
and  the  following  thi'ee  types  were  used  with  success: 

1.  Four  ounces  of  chlordane  added  to  one  gallon  of  black  creosote. 

2.  One  ounce  of  chlordane  to  one  (|uart  of  motor  oil. 

3.  Fifty  percent  wettablc  DDT  nuxed  to  a  paste  with  water. 

The  honey  bees  attached  their  comb  to  the  lid  of  the  box,  as  shown 
in  Figure  17,  so  only  the  lid  of  a  box  was  treated  with  repellents.  The 
lids  of  all  boxes  were  treated  during  the  first  check  of  each  year  after 
1953.  Honey  bee  usage  was  reduced  to  a  minimum  after  the  repellents 
were  used.  During  the  1953  nesting  season  35  percent  of  the  boxes  were 
occupied  by  honey  bees.  After  a  winter  application  of  rej^'Ucuts  less 
than  two  percent  of  the  boxes  contained  bees  in  the  1954  nesting 
season. 

Female  wood  ducks  showed  no  aversion  to  occupying  a  treated  box ; 
nest  abandonment  due  to  the  repellents  never  occurred. 

The  use  of  repellents  will  be  a  necessity  in  nest  box  programs  in  the 
Sacramento  and  San  Joacpiin  VaHeys  where  the  majority  of  the  bee 
usage  occurred. 

Some  states  now  have  gone  into  })rograms  using  metal  boxes.  These 
boxes  are  cylindrical  in  shape  and  are  constructed  of  galvanized,  sheet 
metal,  cold  air  pipe.  They  were  designed  to  reduce  nest  predation  and 
to  increase  the  durability.  Although  metal  boxes  were  not  used  in  tit  is 
study,  they  should  be  considered  in  any  future  programs. 


THE   WOOD   DUCK    IN    CALIPOKXIA 


267 


:«* 


FIGURE    17.      The    lid    of    a    nest    box    with    attached    honey    comb.    The    lids    were    treated    with 

repellent  to  minimize  this  usage. 


268  CALIFORNIA  FISH   AND  GAME 

CONCLUSIONS 

It  was  coiicludcd  that  nest  boxes  eould  have  a  d(^finite  beariii<i'  on 
llir  number  of  wood  dneks  prodneed  in  California  each  year.  A 
eoortlinated  prourani  conld  lie  int(><irated  into  tbe  unit  manao-ement 
system  used  by  tlie  I'alit'ornia  Depai-tment  of  Fisli  and  Game  with 
littk^  eonfliet  of  j)resent  duties.  Unit  managers  eould  guide  the  et¥orts 
of  boy  seout  groui)s  and  sportsmen  clubs  interested  in  enhancing 
tlie  liabitat  of  Avood  ducks.  The  installation  of  boxes  eould  be  aeeom- 
jdislied  during  slack  work  periods  and  the  checking  of  success  carried 
in  a  short  period  during  the  spring. 

If  a  sufficient  iinmber  of  boxes  could  be  installed,  breeding  popula- 
tion trends  could  be  correlated  with  the  Avood  duck  usage  in  the 
nest  boxes. 

SUMMARY 

1.  Information  is  ju-esented  on  the  early  history  and  abundance  of 
the  wood  duck  in  California.  Destruction  of  habitat  and  overshooting 
caused  the  early  decline  in  numbers  of  wood  ducks.  Hunting  restric- 
tions have  resulted  in  a  partial  recovery  of  the  sj^ecies. 

2.  The  summer  range  extends  over  much  of  California  north  of  the 
Tehachapi  Mountains.  The  breeding  po]iulation  was  estimated  at  1,500 
pairs.  California  is  the  major  wintering  area  for  wood  ducks  on  the 
Pacific  Coast.  Central  California  furnishes  habitat  for  most  of  the 
estimated  wintering  pojnilation  of  about  55,400  wood  ducks. 

3.  A  five  year  study,  1952-56,  was  conducted  to  determine  the  feasi- 
bility of  a  nest  box  program. 

A  total  of  152  boxes  was  installed  and  42  percent  were  used  an- 
nually by  wood  ducks. 

Seventy-six  percent  of  the  nests  hatched  successfully.  The  average 
clutch  size  of  successful  nests  was  13.3  eggs.  Dump  nests  averaged 
28.5  eggs  per  nest. 

Desertion  was  recorded  in  16  percent  of  the  nests;  destruction  oc- 
curred in  eight  percent  of  the  nests. 

4.  A  total  of  119  boxes  (31  percent)  was  occupied  by  species  other 
than  wood  ducks.  Sparrow  hawks,  honey  bees  and  screech  owls  were 
most  commonly  found  using  the  boxes. 

5.  An  average  of  11  percent  of  the  boxes  was  found  to  be  non- 
functional each  year. 

6.  Adequate  maintenance  must  be  included  in  any  program  of 
nesting  box  installation. 

ACKNOWLEDGMENTS 
The  success  of  the  nest  box  study  was  due  largely  to  the  efforts 
of  many  employees  of  all  branches  of  the  California  Department  of 
Fish  and  Game.  All  personnel  of  Federal  Aid  in  Wildlife  Kestoration, 
Project  W30R,  assisted  throughout  the  study.  Richard  Robinson  of 
Fresno  State  College  located  many  of  the  nest  box  sites  and  re- 
corded information  on  the  wood  duck  in  the  San  Joaquin  Valley. 
Humboldt  State  College  students  assisted  with  construction  and  in- 
stallation of  the  boxes  in  Humboldt  County.  Appreciation  is  due  to 
the  members  of  the  Pacific  Flyway  Technical  Committee  and  especially 
Chester  Kebbe  of  Oregon,  Robert  Salter  of  Idaho,  Robert  Jeffery  of 


THE   WOOD   DUCK   IN    CALIFORNIA  269 

Washington,  Ron  Mackay  of  British  Colnmbia,  and  Dwight  Stoek- 
stad  of  Montana,  who  compiled  popnhition  data  for  their  respective 
states.  Special  thanks  are  given  lo  the  landowners  thi-ongliont  the  State 
who  pci'Hiit  ted   iiuresti'ictcd  ficccss  lo  tlicir  land  dnring  the  stndy. 

LITERATURE  CITED 
American  Ornithologists  Union 

1957.   Clieck-list   of  Nortli   Anu'i-icini    liinls.    Kiltli    cd.,   Tlic   Lord   T.iilt  iinor."    T'n'ss 
Inc.,  Baltimore,  691  pp. 

Anonymous 

1030.   Wood    Ducks — ITow    i,>    disliuKuisIi    llinii.    Talif.    Fisli    .-ind    flanie,    vol.    If., 
no.  4,  p.  342. 

Crissey,  W.  F. 

1959.  1959   Status  report  of  waterfowl,  Wildlife   No.  45.    U.    S.   Fish   and    Wildl. 
Serv.,   Spec.   Kci.  Rpt.,  Wash.  25,  D.  C,  Multilith   1(t9  i.p. 

Fisher.  A.  K. 

1920.    In  jMeiiKii'iain  :  Lyman  lieldinj;-,  .\\\k,  \iil.  37,  no.  1.  i)p.  33-45. 

Grinnell,  .Toseiih 

1915.   A    distril)utional    list    of    tlie    birds    of    ( 'aliforiiia.    I'.-icilic    Coast    Avifauna, 
no.  11,  217  pp. 
Grinnell,  Joseph  and  Harold  C.  Bryant 

1915.  Calif.  Fish  and  Game,  vnl.'l,  no.  2,  pj).  49-.52. 
Kennedy,  C.  B.  II. 

1859.  Report  on  birds  collected   on   the  route.   Pacific  Railroad   Reports,    vol.    10, 
pt.  6,  no.  3,  War  Department,  Wasli.,  !>.  C.,  pp.  11-35. 

Mailliard,  Joseph 

1911.  Odds  and  ends.  Condor,  vol.  13,  no.  2,  p.  49. 

Massachnsetts  Division  of  Fisheries  and  (lame 

Undated.  Sununary  of  wood  duck  research  methods.  Mimeo.,  14  pp. 

Stoner,  Emerson  A. 

1940.   AVood   ducks   in    Solano   and  Napa   Counties,   California.    Condor,   vol.   42, 
no.  3,  p.  170. 

Townsend,  Charles  H. 

1887.   Field    notes    on    the    mamnntls,    birds    and    reptiles    of    iiorllier-n    r.-ilifornia. 
Rroc.  U.S.N.M.,  vol.  10,  pp.  159-241. 


2—17250 


USE  OF   DESERT  SHRUBS   BY  JACKRABBITS 
IN   NORTHEASTERN   CALIFORNIA' 

STURGIS   McKEEVER 
Department  of  Zoology,  University  of  California,  Davis 

and 

RICHARD   L.   HUBBARD 

Pacific  Southwest  Forest  and  Range  Experiment  Station 

U.S.  Forest  Service,  Berkeley 

INTRODUCTION 

Obsorvations  by  tbe  antbors  wbih^  doing  field  Avork  indicated  tbat  tbe 
jaekrabbit  (Lepus  calif ornkus)  approaebed  or  reaebed  a  peak  in  popu- 
lation density  in  1958-59  in  northeastern  California.  Tbese  observa- 
tions were  substantiated  by  tbe  number  of  requests  received  by  the 
Lassen  County  Agricultural  Commissioner  for  poison  for  jackrabbits. 
Requests  reached  a  maximum  number  in  1958-59  and  decreased  in 
1959-60.  Furthermore,  those  ranchers  who  requested  poison  in  1959-60, 
reported  that  jackrabbits  were  much  less  abundant  than  they  were 
the  previous  year. 

Particularly  heavy  concentrations  of  rabbits  were  noted  on  certain 
areas,  and  desert  shrubs  on  these  areas  were  used  intensively  for  food 
by  the  rabbits.  To  determine  the  degree  and  type  of  use  being  made 
of  the  various  si)ecies  of  shrubs,  a  study  was  made  at  Turtle  Point, 
near  Herlong,  Lassen  County,  California.  The  area  lies  at  the  western 
edge  of  the  Great  Basin  and  immediately  east  of  the  Sierra  Nevada 
escarpment. 

STUDY  METHODS  AND   DESCRIPTION  OF  VEGETATION 

A  transect  of  sixteen  1/20-acre  plots  was  located  at  right  angles  to 
an  east  facing  slope,  extending  from  an  elevation  of  4,120  feet  down 
to  4,065  feet  (Figure  1).  A  random  starting  point  was  chosen  and 
l)l()ts  were  taken  at  tAvo-chain  int(>rvals  along  a  predetermined  bearing. 

Jackrabbit  use  consisted  of  browsing  and  girdling.  Browsing  was 
tabulated  as  light  (trace  browsing),  moderate  (up  to  14  of  main 
branches  browsed),  and  heavy  (14  or  more  of  main  branches  browsed). 
Girdling  was  tabulated  as  tiie  percentage,  to  the  nearest  10  percent, 
of  main  live  stems  showing  some  degree  of  girdling.  The  degree  of  both 
types  of  use  for  a  given  plant  was  based  upon  a  subjective  estimate  by 
the  senior  author. 

Vegetation  on  the  area  was  composed  principally  of  eight  species  of 
shrubs.  At  the  highest  elevation,  desert  peach  (Frunus  under sonii)  was 
the  predominant  species,  with  some  big  sagebrush  (ArUmisia  triden- 
tata)  and  bitterbrush  (PursMa  tridentata)  present.  As  the  elevation 

1  Submitted  for  publication  January,  lOfiO. 

(271) 


272  CALIFOKXIA   FISn   AND   GAME 


FIGURE   1.      View    of    area    where    study    was    made.    That    portion    of    the    area    immediately 
beyond  the  shrub  type  was  covered  with  a  pure  stand  of  winterfat.  August,  1959. 

decreased,  composition  of  the  vegetation  changed ;  at  the  lowest  eleva- 
tion was  a  pure  stand  of  four-winged  saltbush  (Afriplex  cancscens) 
(Table  1).  Beyond  the  saltbush,  but  not  included  in  the  transect,  was 
a  pure  stand  of  wdnterfat  (Eurotia  lanata). 

RESULTS  AND   DISCUSSION 

Girdling  was  confined  principally  to  hopsage  (Grayia  spiiiusa), 
desert  peach,  and  horsebrush  (Tetradymia  glahrata)  (Figure  2).  Hop- 
sage  showed  heaviest  use  with  79  percent  of  the  plants  showing  some 
girdling,  and  all  the  main  stems  girdled  on  51  percent  of  the  jilants 
(Figure  3).  Desert  peach  showed  some  girdling  on  72  percent  of  the 
plants,  and  17  percent  had  some  use  on  all  the  main  stems. 

All  of  the  large  main  stems  on  many  plants  had  been  killed  by 
girdling,  and  new  sprouts  had  developed  from  the  roots.  Only  16  per- 
cent of  the  horsebrush  had  any  girdling. 

Minor  girdling  was  found  on  three  other  species.  One  bitterbrush 
plant  showed  less  than  10  percent  use,  two  rabbitbrush  plants  (Chry- 
soiliamnus  luiKseosns)  showed  10  and  20  percent  use,  and  one  four- 
winged  saltbush  showed  50  percent  use. 

All  of  the  eight  principal  species  of  shrubs  showed  some  browsing 
(Figure  4).  Four-winged  saltbush  and  hopsage  had  some  browsing  on 
all  plants,  with  79  and  70  percent,  respectively,  in  the  heavily  browsed 


USE  OP  SHRUBS  BY   JACKRABBITS 


273 


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274 


CALIFUKXIA    FISH    AM)    (lA.Mt: 


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PERCENTAGE    OF    MAIN    STEMS  GIRDLED 


FIGURE    2.      Degree   of   girdling    of   desert   shrubs    by   jackrabbits    near    Herlong,    Lassen    County, 

California. 


class  (Figures  5  and  6).  Seventy-six  percent  of  the  bitterbrush  were 
browsed,  but  none  fell  in  the  heavily  browsed  class.  Desert  peach 
showed  some  use  on  72  percent  of  the  plants,  with  30  percent  heavily 
browsed.  Sixty  percent  of  the  big  sagebrush  were  browsed,  and  26  per- 
cent showed  heavy  use. 

Only  minor  browsing  was  found  on  the  other  three  principal  species. 
Thirty  percent  of  the  horsebrush  plants  showed  use,  but  only  2  per- 
cent were  in  the  heavy  class.  Chrysofhamnus  nauseosus  showed  some 
browsing  on  34  percent  of  the  plants,  with  12  percent  in  the  heavy 
class.  Twelve  percent  of  the  C.  viscidifloriis  plants  had  been  used  and 
three  percent  were  in  the  heavy  use  class. 

No  tabulation  was  made  of  browsing  of  winterfat,  but  it  was  esti- 
mated that  over  90  percent  of  the  plants  near  the  shrub  type  showed 
some  use.  In  this  type,  as  in  the  shrub  type,  rabbit  pellets  were  very 
abundant  (Figure  7).  Use  of  winterfat  diminished  as  the  distance 
from  the  shrub  type  increased,  probably  because  winterfat  does  not 
provide  adequate  cover. 

It  is  conceivable  that  the  composition  of  the  desert  shrub  type  could 
be  altered  by  jackrabbit  use  of  the  intensity  described  here.  Browsing 
and  girdling  of  hopsage  and  repeated  girdling  of  desert  peach  could 
result  in  partial  elimination  of  these  two  species.  Heavy  browsing  of 


USE  OF   SHRUBS   BY   JACKRABBITS 


275 


FIGURE  3.      Girdling  of  hopsage  by  jackrabblts.  July,  1959. 


■i 


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TETRAD  VMI«       I  GRATIA  I  PURSHIA  1  P  RUNUS  I         ARTIMISIA         I  CHRYSOTHAMNUS  I  CHRTSOTHAMNUS    I         ATRIPLEX  1 

CLABRATA  SPIROSA  TRIDENTATA  ANDERSONII  TRIDENTATA  NAUSEOSUS  VISCIDIFLORUS  CANESCENS 

FIGURE.    4.      Degree  of  browsing  of  desert  shrubs  by  jackrobbits  near   Herlong,   Lassen   County, 

California. 


276 


CALIFORNIA  FISH  AND  GAME 


FIGURE   5.      Four-winged  saltbush  showing  extremely  heavy  browsing  by  jackrobbits.  July,  1959. 


FIGURE  6.      Hopsoge  which  has  been  heavily  browsed  by  jackrobbits.  July,  1959. 


USE   OP   SHRUBS   BY   JACKRABBITS 


277 


FIGURE  7.  Winterfat  which  has  been  heavily  browsed  by  jackrabbits  Notu  ihe  clipped  but 
uneaten    items    on    the    ground    and    the    heavy    concentration    of    rabbit    pellets.    August,    1959. 

four-winged  saltbusli  conld  result  in  suppression  of  this  species.  The 
other  species  probabl^y  would  be  little  affected  once  established,  but  a 
high  population  of  jackrabbits  could  prevent  survival  of  seedlings. 


SUMMARY 

High  densities  of  jackrabbits  were  observed  in  northeastern  Cali- 
fornia in  1958-59,  and  on  some  areas  desert  shrubs  were  used  inten- 
sively for  food  by  the  rabbits.  A  study  was  made  to  determine  the 
degree  and  type  of  use. 

Girdling  occurred  principally  on  hopsage,  desert  peach,  and  horse- 
brush;  the  degree  of  use  was  79,  72,  and  16  percent,  i-espectivoly.  All 
main  stems  were  girdled  on  51  jiercent  of  the  hopsage  plants. 

All  of  the  principal  shrub  species  exhibited  some  browsing.  Four- 
winged  saltbush  and  hopsage  were  the  species  most  used ;  all  plants 
were  browsed  to  some  degree,  and  79  and  70  percent,  T'esi)ectively,  Avere 
heavily  used.  Seventy-six  percent  of  the  bitterbrush,  72  percent  of  the 
desert  peach  and  60  percent  of  the  big  sagebrush  were  browsed,  but 
heavy  browsing  occurred  on  no  bitterbrush,  on  .'30  percent  of  desert 
peach,  and  on  26  percent  of  big  sagebrush.  Less  tban  .SO  percent  of  the 
horsebrush  and  rabbitbrush  were  browsed. 

Use  of  desert  shrubs  for  food  by  jackrabbits,  at  the  rate  observed 
during  this  study,  could  result  in  a  change  in  composition  of  the  type. 
Hopsage,  desert  peach  and  four-winged  saltbush  would  be  the  species 
most  likely  to  be  eliminated  or  suppressed. 


THE  AGE  AND  GROWTH   OF  STRIPED   BASS 
(Roccus  Saxotilis)  IN   CALIFORNIA' 

JOHN    B.    ROBINSON 

Inland  Fisheries  Branch 

California  Department  of  Fish  and  Game 

INTRODUCTION 

By  far  tlie  most  important  population  of  striped  bass  in  California 
is  centered  in  the  San  Francisco  Bay  area  and  the  lower  reaches  of  the 
Sacramento-San  Joaqnin  river  system. 

Over  the  years,  angling-  pressure  on  this  population  has  increased 
markedly,  and  many  changes  have  occurred  in  the  environment  of  this 
|)opular  game  fish.  An  understanding  of  the  effects  of  these  factors  on 
the  population  is  highly  desirable  for  management  purposes.  A  thorough 
knowledge  of  the  life  history  of  the  fish  is  essential  in  achieving  such 
understanding,  and  age  and  growth  characteristics  form  an  important 
phase  of  life  history. 

The  only  previous  extensive  growth  study  of  this  popidation  was 
made  by  Scofield  (Ifl.'U).  Length-weight-age  relationships  were  de- 
termined by  Clark  (1938),  using  Scofield 's  age  material.  The  present 
angling  regulation  fixing  the  niininimn  lengtli  limit  at  IG  inches  is 
based  on  this  early  work. 

Since  the  changes  in  fishing  ])ressui'('  and  Ihc  eiiviroiunenl  tlial  have 
occurred  during  the  intervening  years  conld  have  affected  the  growth 
rate,  and  in  the  light  of  the  previously  stated  considerations,  another 
age  and  growth  study  was  initiated  during  the  fall  of  1957. 

METHODS  AND  MATERIALS 

A  total  of  1,089  scale  samples  was  collected  from  striped  bass  caught 
by  angling  in  San  Pablo  Bay  and  the  lower  SacranuMito-San  .Toa(|nin 
Delta  area  during  the  fall  of  1957  and  summer  and  fall  of  li)58.  Sevei-al 
scales  were  taken  from  the  left  side  of  each  fish  in  the  area  above  the 
lateral  line  and  below  the  origin  of  the  second  dorsal  fin.  Key  scales 
were  not  used.  Fork  length,  weight,  and  sex  were  recoi-ded  for  each 
fish.  The  sex  was  determined  by  examination  of  the  gonads. 

In  the  laboratory,  three  scales  that  were  not  torn  or  regenerated 
were  selected  from  each  sample.  These  were  cleaned  and  impressed  on 
1  X  8  X  0.080-inch  cellulose  acetate  slides.  Scales  from  188  fish  were 
unusable,  leaving  951  for  the  study. 

An  Eberbach  scale  projector  with  a  32mm.  IMaci-o  Tessar  lens  pro- 
viding a  magnification  of  42x  was  used  to  age  and  measure  the  scales. 
They  were  aged  by  counting  annuli,  which  Scofield  had  shown  to  be 
valid.  The  locations  of  the  focus,  the  annuli,  and  the  scale  margin  for 


1  Submitted  for  pul)lication  February,  lOfiO.  This  work  was  performed  as  part  of 
Dingell-.Iohnson  Project  California'  F-9-R,  "A  Study  of  Sturgeon  and  Striped  Bass," 
Supported  by  Federal  Aid  to  Fish  Restoration  funds. 

(  279  ) 


280 


CALIFORNIA  FISH   AND  GAME 


each  scale  -  Avere  marked  on  a  paper  strip  for  later  use  in  determining 
the  body  lenp'th-scale  length  rclationsliip  and  in  back  ealenlating 
growth.  All  scales  were  aged  independently  by  two  men,  and  the 
few  scales  on  w'hicli  they  could  not  agree  were  rejected  for  growth 
calculations. 

The  radius  of  each  scale  Avas  measured  to  the  nearest  millimeter, 
and  averaged  for  the  three  scales  from  each  fish.  The  fish  were  then 
grouped  by  scale  radius  intervals  of  one  centimeter  and  the  mean  body 
length  for  each  group  was  found  using  the  method  of  Whitney  and 
Carlander  (1956).  The  body  length-scale  length  relationship  was  then 
determined  by  plotting  the  mean  fork  length  of  the  fish  in  each  scale 
measurement  group  against  the  scale  length  and  fitting  a  regression  line 
to  the  data. 

The  back  calculation  of  growth  was  accomplished  using  a  direct 
proportion  nomograph  corrected  for  the  Y  axis  intercept. 

•The  length-weight  relationship  was  determined  by  grouping  the  fish 
by  one-inch  body  length  intervals  and  computing  the  mean  fork  length 
and  weight  of  the  fish  in  each  interval.  These  averages  were  then  con- 
verted into  logarithms  and  the  linear  regression  was  used  following 
the  method  described  by  Sigier  (1953). 

-  All  scale  measurements  were  made  along   the   radius  from   the   focus  to  the  center 
anterior  edge. 


JD 

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ENLARGED   SCALE   RADIUS    MEASUREMENT  IN  CENTIMETERS 


40 


50 


FIGURE   1.     Striped  bass  body  length-scale  length  relationship. 


AGE   AND   GROWTH   OF   STRIPED   BASS 


281 


RESULTS 
Body  Length-Scale  Length  Relationship 
The  relationship  between  body  length  and  scale  length  is  shown  in 
Fig-nre  1.  A  straight  line  fitted  to  the  points  by  the  least  squares 
method  is  described  by  the  formula  Y  =  0.97  +  0.77X,  where  Y  is  the 
fork  length  of  a  fish  in  inches,  X  is  the  enlarged  scale  radius  measure- 
ment in  centimeters,  and  0.97  is  the  Y  axis  intercept  of  the  regi-ession 
line  in  inches.  Since  the  smallest  fish  sampled  were  three  inches  long, 
tlie  Y  intercept  is  an  artificial  value  significant  only  for  back  calcu- 
lating growth  and  is  not  necessarilj^  the  body  length  at  time  of  scale 
formation.  The  linear  relationship  between  scale  length  and  body  length 
indicates  that  scale  length  and  body  length  of  striped  bass  increase 
proportionately  at  least  from  H  inches  to  34  inches.  Scofield  (1931) 
and  ^lerriman  (1941)  also  found  a  proportional  relationship  within  the 
size  ranges  they  studied. 

Growth 

The  growth  histories  of  all  fish  of  ages  II  through  IX  were  calcu- 
lated. Age  I  fish  were  not  used  because  of  the  difficulty  encountered 
in  determining  sex.  The  mean  length  at  the  end  of  each  year  of  life 
was  calculated  separateh^  for  each  fish,  and  these  lengths  were  aver- 


UJ 

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FIGURE  2.      Growth   of   striped    bass   as   calculated    from   scales.    Upper    lines    (A)   show   rate   of 
growth.  Lower  lines  (B)  indicate  annual  growth  increment. 


282 


CALIFORNIA  FISH   AND  GAME 


average  annual  increments  of  growth  were  then  de- 


aged  to  get  a  iiu-aii  Icngtli  at  the  end  of  each  year  of  life  for  each  age 
jjronp  for  each  sex  '/lables  1  and  2).  The  means  for  each  year  of  life 
wer«  then  averaged  by  sexes  to  get  the  weighted  ^rand  averau'e  calcu- 
lated length.  The 
termined  for  each  year  of  life  (Tables  1  and  2). 

These  data  indicate  that  male  and  female  striped  bass  grow  at  the 
same  rate  for  the  first  three  years  of  life.  >Subsequently,  females  grow 
faster.  The  greatest  difference  in  annual  growth  was  reached  at  ages 
VII  and  VIII,  when  it  was  3.0  inches  and  3.3  inches,  respectively 
(Figure  2).  (Age  VIII  is  based  on  a  sample  of  only  five  fish,  so  little 
reliance  can  be  placed  in  the  calculated  difference  at  that  age.)  The 
greatest  annual  growth  of  both  males  and  females,  5.7  inches,  occurred 
in  the  second  year  of  life  (Tables  3  and  4,  Figure  2). 

The  validity  of  back  calculating  growth  is  confirmed  by  the  similarity 
between  measured  lengths  at  capture  and  calculated  lengths  for  fish  of 
the  same  age  groups  (Table  5).  Most  of  the  fish  were  collected  in  the 
fall,  after  most  of  their  year's  growth  was  completed,  but  before  the 
annulus  was  formed.  Therefore,  measured  lengths  were  compared  with 
calculated  lengths  of  fish  a  year  oldei-. 

The  discrepancy  between  the  third  year  growth  increments  found  by 
the  two  methods  was  caused  by  biased  sampling  of  age  I-|-  and  II-j- 
fish.  Age  I  fish  were  collected  in  August,  before  their  annual  growth 
was  completed.  Moreover,  most  age  II  fish  were  from  the  upper  half  of 


+  15 


FIGURE   3.      Percentage  deviation  from  the  mean  annual  growth  Increment  of  striped  bass. 


AGE  AND  GROWTH   OF   STRIPED  BASS 


288 


tlie  leiiyth  distribution,  siiu-c  fish  in  the  lower  half  of  the  leiiyth  distri- 
bution were  protected  by  the  16-inch  minimum  size  limit  when  these 
samples  were  taken. 

Annual  Fluctuations  in  Growth  Rate 

To  determine  annual  iiuctuations  in  the  growth,  the  percentage  de- 
viations from  the  mean  annual  increment  were  calculated  according  to 
the  method  described  by  llile  (li)41),  using  the  mean  annual  increments 
in  Tables  1  and  2.  All  age  groups  were  weighted  equally.  The  period 
1949  to  1951  was  eliminated  from  the  calculations  because  the  age 
groups  VII,  VIII,  and  IX  are  poorly  represented. 

The  percentage  deviations  for  the  1952  to  195()  pei'iod  are  shown 
in  Table  6  and  Figure  8.  Growth  was  slow  in  1952,  and  faster  than 
average  the  next  three  years,  with  the  maximum  for  the  period  oc- 
curring in  1953.  From  1953  to  1956  there  was  a  steady  decline  in 
growth. 

These  data  show^  that  there  are  annual  fluctuations  in  growth.  How- 
ever, so  few  years  of  data  are  involved  that  the  significance  of  the 


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FORK    LENGTH  IN   INCHES 
FIGURE  4.      Length,  weight,  and  age  relationship  of  striped  bass. 


30 


35 


284 


CALIFORNIA   FISH    AM)   GAME 


Unetnations  cannot  be  determined.  ^Moreover,  data  to  indicate  the  causes 
of  tlie  tiuctnations  are  not  available. 

Length-Weight  Relationship 

The  lenp'th-weight  relationship  is  described  by  the  equation  log 
W  =  —2.1. 398  +  3.0038  long  L,  and  this  line  is  plotted  in  Figure  4.  The 
annual  weight  increments  are  shown  in  Figure  5.  This  relationship  is 
similar  to  the  results  of  three  other  striped  bass  length-weight  studies 
(Clai-k,  1!)38;  Merriman,  1941;  Morgan  and  Gerlach,  1950). 

Comparisons  of  Growth 

Previous  striped  bass  growth  studies  have  been  made  on  the  At- 
lantic Coast  (Pearson,  1938;  Merriman,  1941;  Tiller,  1950;  Vladykov 
and  Wallace,  1952;  Stevens,  1957),  and  also  in  California  (Scofield, 
1931)  and  Oregon  (Morgan  and  Gerlach,  1950).  Reported  growth  rates 


40 


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FIGURE   5.      Annual  weight  increment  of  striped  bass. 


AGE   AND  GROWTH   OF   STRIPED  BASS 


285 


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AGE   AND  GROWTH   OP   STRIPED   BASS 


287 


are  seen  to  be  p-enerally  similar  to  those  found  in  the  present  study 
(Table  7),  with  the  exception  of  the  work  of  Stevens  (1957).  However, 
the  latter  study  is  not  completely  analogous,  since  it  involved  the  land- 
locked population  in  Santee-Cooper  Reservoir. 

Tlie  ]n'eseiit  study  shows  that  there  has  been  a  sif2:iiifi("ant  increase 
in  the  growth  rates  of  the  California  bass  since  the  work  of  Scofield 
(Tables  3  and  4).  This  increase  occurs  after  the  second  year,  and  it  is 
greater  in  females  than  in  males.  For  females,  the  greatest  difference 
is  2.8  inches  at  six  years  of  age,  while  for  males  the  greatest  difference 
is  2.3  inches  at  both  six  and  seven  years  of  age.  This  represents  ap- 
proximately a  10  percent  increase  in  length  and  a  25  percent  increase 
in  weight. 

TABLE  3 
Comparison  of  Growth  of  Male  Striped  Bass  in  1930  and  1957-58 


Mean  calculated  fork  length 

Mean 

"annual  growth 

1930 

1957-58 

Differ- 
ence 
between 
1957-58 
and 
1930 

1930 

1957-58 

Differ- 
ence 

Year  of  life 

Num- 
ber of 
fish 

Length 

(inches) 

Num- 
ber of 

fish 

Length 

(inches) 

between 

1957-58 

and 

1930 

1.     

35 
35 
35 
35 
34 
18 
12 

4.2 
9.9 
14.6 
17.5 
20.3 
22.2 
24.1 

385 

385 

354 

164 

75 

36 

16 

5 

2 

4.1 
9.8 
15.2 
19.4 
22.3 
24.5 
26.4 
28.2 
30.0 

—0.1 
—0.1 
*-|-0.6 
*-|-1.9 
*-f-2.0 
*-|-2.3 
*-|-2.3 

4.2 
5.7 
4.7 
2.9 
2.4 
1.9 
1.9 

4.1 
5.7 
5.4 
4.2 
2.9 
2.2 
1.9 
1.8 
1.8 

0  1 

2 

3                  -    --.    .-      .- 

0 
+  0.7 
+  1.3 
+  0.5 
+  0.3 

0 

4 

5 

6                      ---    . 

7 

8     -    

9 

*  statistically  significant  increase  in  growth. 


TABLE  4 
Comparison  of  Growth  of  Female  Striped  Bass  in  1930  and  1957-58 


Mean  calculated  forlv  lengtli 

Mean  annual  grow  tli 

1930 

1957-58 

Differ- 

Differ- 

ence 
between 

ence 

between 

Num- 

Num- 

1957-58 

1957-58 

ber  of 

Length 

ber  of 

Length 

and 

and 

Year  of  life 

fish 

(inches) 

fish 

(inches) 

1930 

1930 

1957-58 

1930 

1 

43 

4.2 

295 

4.1 

—0.1 

4.2 

4.1 

—0.1 

2 

43 

9.7 

295 

9.8 

+  0.1 

5.6 

5.7 

+  0.1 

3 

43 

14.6 

281 

15.3 

*+0.7 

4.8 

5.5 

+  0.7 

4 

43 

18.1 

131 

19.7 

*+1.6 

3.5 

4.4 

+  0,9 

5 

43 

21.3 

49 

23.4 

*  +  2.1 

3.2 

3.7 

+  0.5 

6 

33 

24.1 

25 

26.9 

*  +  2.8 

2.7 

3.5 

+  0.8 

7 

21 

26.8 

13 

29.4 

*  +  2.6 

2.7 

2.5 

—0.2 

8 

5 

31.5 

2.1 

9 -__        -__   - 

3 

32.9 

1.7 

*  statistically  significant  increase  in  growth. 


288  CALIFORNIA  FISH   AND  GAME 

TABLE  5 

Comparison  Between  Measured  Fork  Lengths  of  Striped  Bass  Collected  in  1957-58 
and  Calculated  Fork  Lengttis 


Males 

Females 

Mean  length 

Mean  calculated 

Mean  length 

Mean  calculated 

at  capture 

length 

Age 

at  capture 

length 

(inches) 

(inches) 

group 

(inches) 

(inches) 

4.1 

I 

4.1 

8.6 

9.8 

II 

8.6 

9.8 

16.2 

15.2 

III 

16.4 

15.3 

19.4 

19.4 

IV 

20.0 

19.7 

22.4 

22.3 

V 

23 . 5 

23.4 

25.0 

24.5 

VI 

25.9 

26.9 

26.2 

26.4 

VII 

28.9 

29.4 

27.7 

28.2 

VIII 

30.6 

31.5 

29 . 0 

30.0 

IX 

33.4 

32.9 

31.1 





33.9 



TABLE  6 
Percentage  Deviation  from  the  Mean  Annual  Growth  of  Striped  Bass,  1952-1956 


1952 

1953 

1954 

1955 

1956 

—  1.8 

—  17.1 

—9.5 

+  2.7 
+  7.8 
+  5.3 

+  3.6 
—  1.9 
+  0.9 

—1.4 
+  2.0 

+  0.3 

—1.3 

Females 

—8.0 

—4.7 

TABLE  7 
Growth  of  Striped  Bass  in  Various  Waters,  Sexes  Combined 


LENGTH  IN  INCHES 

Merriman 

(1941); 

mean 

calculated 

Morgan 

Present 

fork  length 

and 

study, 

Schofield 

Pearson 

to  4  years, 

Gerlach 

Stevens 

1957-58; 

(1931); 

(1938); 

mean  fork 

(1950); 

(1957); 

mean 

mean 

fork 

lengths 

mean  fork 

mean 

calculated 

calculated 

length 

of  age 

lengths 

calculated 

fork 

fork 

frequency 

classes 

of  age 

total 

Year  of  life 

lengths 

lengths 

distributions 

5  to  9  years 

classes 

lengths 

1..   ..   

4.1 
9.8 

4.2 
9.8 

4.0 
10.0 

4.9 
9.3 



8.5 

2 

15.7 

3 

15.3 
19.6 

14.6 

17.8 

15.0 
18.5 

14.4 
17.7 

14.5 
19.0 

19.8 

4 

22.9 

5 

22.9 

20.8 



20.9 

22.7 

25.8 

6.... 

25.7 

23.2 



24.0 

25.0 

28.5 

7 

27.9 

25.4 



27.0 

27.3 

30.2 

8 

29.9 
32.3 





29.5 
32.3 

28.8 
30.0 

9 

AGE  AND   GROWTH   OP   STRIPED  BASS  289 

There  are  many  possible  eaiisos  for  this  increase  in  growth  rate,  but 
the  available  data  are  insufficient  to  determine  which  ones  are  respon- 
sible. One  of  the  most  logical  explanations  is  that  the  competition  for 
food  has  decreased,  due  to  the  decline  in  the  numbers  of  sti-iped  bass 
during  this  period.  This  decline  in  the  bass  population  is  shown  by  the 
marked  decline  in  catch  per  unit  of  effort  in  the  stri])ed  bass  sport 
fishery  (Calhoun,  1953;  Ryan,  1959;  and  unpublished  data). 

MANAGEMENT  APPLICATIONS 

The  results  of  the  present  study  are  pertinent  to  an  evaluation  of 
llic  increase  in  the  minimum  size  limit  from  12  inches  to  16  inches  made 
in  1956.  These  results  show  that  Clark's  (1938)  finding  that  bass  double 
their  weight  between  12  and  16  inches  is  still  valid.  However,  the  ])resent 
study  indicates  that  this  growth  is  now  accomplished  during  a  shorter 
period  of  time.  Therefore,  the  present  growth  rate  is  even  more  favor- 
able to  the  increase  in  size  limit  than  it  was  thought  to  be  on  the  basis  of 
the  information  that  was  avaiUU)le  wIumi  the  size  limit  was  changed. 

The  threadfin  shad,  Dorosoma  pdcnense,  was  introduced  into  res- 
ervoirs on  the  Sacramento-San  Joaquin  river  system  in  1959,  and  is 
expected  to  become  established  in  many  of  the  areas  now  inhabited 
by  striped  bass.  This  study  will  be  of  value  in  helping  to  determine 
the  effect  of  this  introduction  on  the  striped  bass  population. 

SUMMARY 

Striped  bass  collected  in  1957  and  1958  were  studied  to  determine 
whether  significant  changes  in  the  growth  rate  had  occurred  during 
the  last  30  years.  The  growth  rate  was  determined  by  aging  scales  and 
back  calculating  the  growth.  The  length-weight  relationship  was  also 
determined. 

It  was  found  that  the  growth  rate  is  similar  to  that  found  iu  Cali- 
fornia 30  years  ago,  and  in  most  other  striped  bass  i)opulations.  How- 
ever, it  does  show  that  there  has  been  a  significant  increase  in  the 
growth  rate  of  California  striped  bass  between  the  ages  of  III  and 
VII  during  the  last  30  years.  This  difference  reaches  a  maximum  of 
about  2.5  inches  at  ages  VI  and  VII. 

No  significant  changes  were  found  in  the  length-weight  relation- 
ship, but,  because  of  the  increased  rate  of  growth,  the  mean  weight 
of  bass  at  a  given  age  is  greater. 

The  age  and  growth  data  from  this  study  are  more  favoi-ablc  for 
the  size  limit  increases  made  in  1956  than  the  growth  data  available 
for  evaluation  at  that  time. 

ACKNOWLEDGMENTS 

The  author  wishes  to  thank  Harold  K.  Chadwick  for  his  guidance 
and  helpful  criticisms,  and  to  acknowledge  the  assistance  of  Vincent 
Catania,  William  Kier,  and  Bruce  Eliason,  who  lidped  collect  and 
process  data. 


290  CAMFOKMA  FISH  Axn  r; A:\rE 

REFERENCES 
Callionii.  A.  .1. 

I!jrj3.  Stato-wiilc  Calit'oniia  auulin.i;  est  iiualcs  for  l!)."il.  ("alif.  Fish  and  Uaino, 
vol.  39,  no.  1,  i)p.  KKJ-nS. 

Clark,  G.  II. 

103S.  "Woisht  and  a.ue  (let cnuiiiat  ion  of  striiit'd  liass.  Calif.  Fish  and  Game,  vol. 
2-1.  no.  2,  iqi.  17(>-1  77. 

Hih*.  Ralph 

1!)4].  Afic  and  ,i;ro\vth  of  the  rock  hass.  A  nililoiilifcs  riiprstris  (Rafinesque) ,  in 
Nebish  Lake,  Wisconsin,  ^^'is(•.  Acad.  Sci.,  Arts  and  Let.,  Trans.,  vol.  33, 
pp.  189-337. 

Merrinian.  Daniel 

1941.  Studies  on  the  striped  bass  (Rocriis  snxatilis)  of  the  Atlantic  Coast.  U.  S. 
Fish  and  Wildl.  Serv.,  Fish.  Bull.,  vol.  50,  no.  3-"),  77  pp. 

Morgan,  Alfred  R.,  and  Arthur  R.  Gerlach 

19.jO.  Striiied  Itass  studies  on  Coos  Bay,  Oregon  in  1949  and  19-50.  Oregon  Fish 
Comm.,  Contrib.  no.  14,  31  pp. 

Pearson,  John  C. 

1938.  The  life  history  of  the  striped  bass,  or  rockfish,  lioccus  saxatilis  (Wal- 
baum).  r.  S.  Bur.  Fish..  P.nll..  vol.  49,  no.  28,  pp.  825-851. 

Ryan.  James  H. 

1959.  California  inland  angling  estimates  for  1954,  1956,  and  1957.  Calif.  Fish 
and  Game,  vol.  45,  no.  2,  pp.  93-109. 

Scofield,  Eugene  C. 

1931.  The  striped  bass  of  California  ( Rocvus  Uneutus).  Calif.  Div.  Fish  and 
Game,  Fish  Bull.  29.  84  pp. 

Sigler,  William  F. 

1953.  The  collection  and  interpretation  of  fish  life  history  data.  Pnbl.  by  W.  F. 
Sigler  and  Wildl.  Mangt.  Dept.,  Utah  State  Agric.  College,  Logan,  Utah, 
40  pp.  (mimeo.) 

Stevens,  Robert  E. 

1957.  The  striped  bass  of  the  Santee-Cooper  Reservoir.  South  Carolina  Wildl. 
Res.  Dept.,  Rept.,  21  pp.  (mimeo.) 

Tiller,  Richard  E. 

1950.  A  five-year  study  of  the  striped  bass  fishery  of  Maryland,  based  on  analyses 
of  the  scales.  Publ.  Chesapeake  Biol.  Lab.,  no.  85,  30  pp. 

Vladykov,  V.  D.,  and  D.  H.  Wallace 

1952.  Studies  of  the  striped  bass,  ]\occiis  saxatilis  (Walbaum),  with  special  ref- 
erence to  the  Chesapeake  Bay  region  during  1936-1938.  In:  The  striped  bass, 
Bocciis  saxatilis,  by  Edward  C.  Raney  et  al.,  pp.  132-177.  Bull.  Bingham 
Oceanographic  Collection,  vol.  14,  no.  1. 

Whitney,  Richard  R.,  and  Kenneth  D.  Carlander 

1956.  Interpretation  of  body  scale  regression  for  coiniiutiug  body  length  of  fish. 
Jour.  Wildl.  Mangt.,  vol.  20,  no.  1,  pp.  21-27. 


THE  IMPORTANCE  OF  THE  OCEAN   SPORT  FISHERY 

TO  THE  OCEAN   CATCH  OF  SALMON   IN 

THE   STATES  OF  WASHINGTON, 

OREGON  AND  CALIFORNIA' 

HENRY   O.   WENDLER 

State  of  Washington 

Department  of  Fisheries 

INTRODUCTION 

Commercial  tishiny  for  salmon  in  the  ocean  began  in  the  late  lJ)th 
and  early  2()tli  centuries  when  it  was  found  that  both  chinook  (Onco- 
rhynchus  tshawytscJia)  and  silver  salmon  (0.  kisutcJi)  would  readily 
take  a  trolled  lure  (Van  Hyning,  1951).  Scofield  (1956)  noted  that 
commercial  trolling  through  the  1890 's  amounted  to  little  until  the 
discovery  of  the  mild-curing  process  (about  1898)  following  which  it 
reached  quantity  production  about  1901.  Kauffman  (1951)  stated  that 
Washington  inside  commercial  troll (>rs  gradually  turned  to  more  pro- 
ductive grounds  offshore  after  1917.  These  offshore  trollers  were  ex- 
ceedinglj^  important  to  the  economy  of  many  small  coastal  ])orts  and 
were  instrumental  in  opening  new  small  boat  harbors  along  the  coasts 
of  Washington,  Oregon,  and  California. 

Commercial  trolling  licenses  have  shown  a  general  increase  after 
World  War  II  and  especially  during  the  last  few  years.  Pai't  of  the 
increase  has  been  due  to  the  ease  in  obtaining  licenses  in  some  of  the 
states,  regardless  of  type  of  boat  or  gear.  Both  commercial  aiul  sy)ort 
trolling  may  be  conducted  readily  from  small  boats  wliicli  rc(i\iire  a 
low  original  investment.  The  gear  used  is  comparatively  inexpensive. 
This  manner  of  fishing,  therefore,  has  attracted  many  hundreds  of 
commercial  and  sport  fishermen  to  wat(>rs  adjacent  to  1he  coasts  of  the 
three  aforementioned  states. 

Sport  fishing  for  salmon  in  Washington's  sounds,  bays,  harbors,  and 
rivers  also  dates  back  to  the  late  19th  century  (Pressey,  1958).  How- 
ever, it  was  not  until  the  early  1940's  that  this  salt-watei-  sport  began 
showing  signs  of  becoming  one  of  the  more  important  fisheries  of  this 
state.  Scofield  (ojJ.  cit.)  mentioned  that  salmon  trolling  was  practiced 
in  California  in  the  early  1880 's  by  a  few  sportsmen.  Tiie  real  increase 
began  after  World  War  II.  Prior  to  1951,  except  for  the  Puget  Sound 
region,  salt  water  sport  catches  generally  occurred  either  in  oi-  just  off 
the  various  coastal  river  mouths  during  the  period  when  runs  of  salmon 
were  expected  to  enter  the  rivers  on  their  annual  spawning  migration. 

I  Submitted  for  publication  March,  1960.  Prepared  at  the  request  of  the  Pacific  Marine 
Fisheries  Commission.  Data  supplied  by  the  State  of  Washington  Department  of 
Fisheries,  the  Oregon  Game  Commission,  the  Oregon  Fish  Commission,  and  the 
California  Department  of  Fish  and  Game.  Figures  by  Cliffa  Corson. 

(  291  ) 


292  CALIFORNIA  FISH   AND  GAME 

Prior  to  1950,  I'datix-ely  few  sportsmen  had  fished  for  sahnoii  in  the 
ocean.  The  few  pioneers  in  ili(>se  areas  were  generally  local  people  using 
small  low-i)owered  open  boats  wlio  fished  1lie  "safe"  tides  and  then 
scni-ried  lo  shore  with  their  catches.  The  horsepower  race  which  so 
i-adically  changed  llie  antomotive  field  after  World  War  II  also  af- 
fected inaiinfacturers  of  small  boat  motors.  The  use  of  glass,  metal, 
and  ])lastics  has  revolutionized  the  boat  building  industry.  The  com- 
bination of  dependable  and  powerful  motors  with  larger,  more  sea- 
worthy small  craft  has  permitted  the  sportsman  to  travel  to  offshore 
fishing  areas  that  would  have  been  unsafe  only  a  few  years  ago.  These 
small  craft  have  tended  to  outmunber  the  commercial  boats  and  have 
invaded  coastal  waters  that  formerly  had  been  fished  exclusively  by  the 
commercial  troller. 

The  question  often  arises  in  almost  any  discussion  wdth  commercial 
or  sport  fishing  interests  as  to  the  importance  of  these  two  fisheries  to 
the  total  ocean  catch  of  salmon.  The  primary  difficulty  in  reaching  ade- 
quate conclusions  has  been  a  lack  of  the  mani)ower  needed  to  make 
satisfactory  surveys  of  sport  fisheries.  The  commercial  salmon  catch  for 
the  three  western  states  is  obtained  relatively  easily  since  the  poundage 
of  all  fish  sold  must  be  listed  on  receipt  sheets,  copies  of  which  are  sent 
to  the  managing  agency.  The  number  of  fish  in  the  catch  can  then  be 
determined  by  applying  average  weight  factoi-s  collected  in  the  field. 

The  estimation  of  the  catch  by  sportsmen  has  always  been  fraught 
with  difficulties.  Each  year  the  fishery  may  change  either  in  area  fished, 
duration  of  the  fishery,  or  type  of  lure  used.  The  program  of  sampling 
may  be  limited  in  scope  because  of  manpower  shortages.  These  factors, 
singly  or  in  combination,  may  cause  sampling  errors  which  in  turn 
may  induce  the  catch  estimate  to  be  too  large  or  too  small.  However, 
each  of  the  states  involved  with  ocean  sport  fisheries  has  developed 
certain  methods  to  enumerate  the  catch. 

In  the  sport  fisheries  two  types  of  boats  predominate :  the  skiff  or 
outboard  kicker  boat,  and  the  party  or  charter  boat.  The  party  boats 
usually  have  better  angler  success  because  of  their  greater  cruising 
range  and  experienced  professional  skippers.  They  also  carry  consider- 
ably more  people  than  the  smaller  limited-range  outboards. 

METHODS  OF   ESTIMATING  CATCH   BY  SPORTSMEN 

Washington 

Washington  does  not  issue  a  sport  fishing  license  for  the  taking  of 
salmon.  The  basic  statistic  used  to  estimate  the  sport  catch  depends  on 
the  area  fished  and  the  coverage  desired.  In  and  off  the  mouth  of  the 
Columbia  River  boat  counts  taken  by  the  Coast  Guard  are  used  in 
conjunction  with  personal  interviews  as  the  boats  bring  their  catches  to 
the  landing  areas.  This  particular  sampling  program  is  conducted 
jointly  with  the  State  of  Oregon  since  the  Columbia  River  is  the  state 
boundary  line.  In  the  more  northern  coastal  areas  charter  boat  log 
books,  Coast  Guard  boat  counts,  and  personal  interviews  are  utilized. 
In  the  extreme  northern  sector  (Neah  Bay),  boathouse  report  forms 
are  used  in  conjunction  with  interviews.  Through  the  use  of  these 
methods,  sampling  intensity  has  been  as  high  as  30  percent  of  the  boats 
fishing  in  the  area  (Columbia  River  Progress  Report,  August-Decem- 
ber 1956). 


SPORT  CATCH  OF  OCEAN  SALMON  293 

Oregon 

Oregon  requires  a  sport  fishing  license  for  salmon  and  steelhead  and 
ntilizos  the  punch  card-interview  system  coupled  with  Coast  Giiai-d 
counts  of  boats  in  the  areas  of  fishing  to  enumerate  the  catch.  Tliis 
method  has  been  successful  in  certain  areas  where  the  fishery  is  not 
spread  over  great  distances  and  a  single  species  predoininalcs  in  ihc 
catch.  The  Oregon  punch  card  does  not  differentiate  between  s])ecies 
of  salmon.  Prior  to  1!).j9,  it  Avas  not  retpiired  to  note  on  the  punch  card 
the  number  of  fish  caught  if  the  catch  occurred  in  international 
waters.  This  necessitated  interview  sampling  which  may  have  l)een 
sparse  because  of  limited  maii]M)wer.  By  legislative  act  in  1959,  a  land- 
ing inii)ortation  law  was  enacted  which  requires  that  salmon  caught  in 
international  waters  be  noted  on  the  punch  card  when  the  fishermen 
enter  the  state  waters. 

California 

California  also  requires  a  spoi-t  fishing  license.  Tn  this  state  party 
boat  ski])pei's  are  required  to  send  a  daily  log  of  their  passengers' 
catches  to  the  Department  of  Fish  and  Game.  Spot  checks  are  made 
of  the  accuracy  of  these  reports.  In  1955  and  1956  a  federal  aid  project 
made  a  detailed  study  of  party  boat,  skiff,  and  other  ocean  sport 
salmon  catches,  primarily  by  sampling  the  landings  at  various  ports. 
The  figures  used  in  Table  3  were  obtained  from  these  sources.  In  1955 
and  1956  party  boat  landings  represented  65  percent  of  the  total  ocean 
salmon  sport  landings.  Party  boat  records  were  used  to  calculate  the 
totals  for  other  years.  An  assumption,  based  on  observations  but  not 
samples,  was  used  to  make  these  calculations.  It  was:  party  boat  land- 
ings were  90  percent  of  the  total  from  1947  through  1950,  and  65  per- 
cent from  1951  on  (Eldon  P.  Hughes,  personal  commnnication  March 
1959). 

California  also  has  used  a  post  card  survey  method  to  estimate  the 
trend  of  sport  fishing  catches  during  many  of  the  years  from  1936 
through  1957  (Calhoun,  1950,  1951,  and  1953;  Skinner,  1955;  and 
Ryan,  1959).  In  this  method  questionnaires  are  sent  to  a  random 
sample  of  license  holders.  Post  card  surveys  are  suspect  for  a  variety 
of  reasons,  and  in  this  instance  the  federal  aid  study  of  1955-1956 
demonstrated  that  in  1956  the  post  card  returns  gave  an  estimate  of 
the  ocean  salmon  fishery  that  was  nearly  three  times  what  it  slundd 
have  been. 

OCEAN   CATCH   OF  SALMON   BY  STATES 
Washington 

The  phenomenal  groAvth  of  the  ocean  sport  fishery  in  Washington 
was  further  hastened  by  funds  allocated  by  the  Corps  of  Engineers 
for  building  and  enlarging  small  boat  basins.  Westport,  located  about 
midway  along  the  Washington  coast,  was  relatively  unknown  |)ri(»r 
to  1950.  It  is  now  the  center  of  sport  fishing  activities  and  boasts 
one  of  the  finest  protected  boat  basins  along  the  coast.  Within  a  few 
minutes,  fishermen  leaving  this  small  coastal  town  can  be  in  a  ])osition 
to  intercept  the  salmon  runs  moving  either  north  or  south.  The  ocean 
sport  fisheries  in  Washington  appeared  relatively  minor  until  1952 
(Table  1,  Figures  1  and  2). 


294  CALIFORNIA   PISH    AM)   GAME 

TABLE  1 

Washington  Ocean  Sport  and  Commercial  Troll  Catcties  in  Thousands  of  Fish  and 
Percent  Spor*  Catch  1947  Through  1958 


Commercial  catch 

Sport  catchi 

Total  fish 

Percent  sport 

Year 

Chinook 

Silvers 

Chinook 

Silvers 

Chinook 

Silvers 

Chinook 

Silvers 

1947... 

325 

584 

6 

3 

331 

587 

1.8 

0.5 

1948--- 

286 

746 

6 

3 

292 

749 

2.1 

0.4 

1949.- 

291 

518 

8 

4 

299 

522 

2.7 

0.8 

1950-.. 

257 

551 

17 

13 

274 

564 

6.2 

2.3 

1951.-. 

331 

634 

34 

15 

365 

649 

9.3 

2.3 

1952-.. 

407 

843 

92 

30 

499 

873 

18.4 

3.4 

1953.-- 

419 

665 

46 

50 

465 

715 

9.9 

7.0 

1954--- 

384 

403 

71 

63 

455 

466 

15.6 

13.5 

1955--- 

385 

494 

84 

61 

469 

555 

17.9 

11.0 

1956-.. 

295 

706 

118 

140 

413 

846 

28.6 

16.5 

1957... 

359 

737 

102 

192 

461 

929 

22.1 

20.7 

1958--- 

270 

525 

84 

145 

354 

670 

23.7 

21.6 

1  Columbia  River  spoi t  landings  have  been  equally  cliviiled  between  Washington  and  Oregon  and  aie  ineluded  in 
part  herein. 

The  ocean  sport  catch  for  chinook  salmon  has  ranged  from  a  low  of 
nearly  2  percent  to  a  liig-h  of  nearly  29  percent  of  the  total  catch 
during  the  years  1947  through  1958.  Silver  catches  have  ranged  from 
less  than  1  percent  to  nearly  22  percent  during  the  same  period. 

Oregon 

Ocean  sport  salmon  fishing  in  Oregon  showed  nearly  the  same  mush- 
rooming increase  as  in  the  State  of  Washington.  Sport  fishing  occurred 
on  a  minor  scale  for  a  number  of  years  in  Coos,  AVinchester,  and  Depoe 
bays  but  was  negligible  until  1955  (Table  2,  Figures  1  and  2). 


TABLE  2 

Oregon  Ocean  Sport  and  Commercial  Troll  Catches  in  Thousands  of  Fish  and 
Percent  Sport  Catch  1949  Through  1958 


Commercial  catch 

Sport  catch' 

Total  fish 

Percent  sport 

Year 

Chinook 

Silvers 

Chinook 

Silvers 

Chinook 

Silvers 

Chinook 

Silvers 

1949-.. 

109 

173 

8 

13 

117 

186 

6.8 

7.0 

1950... 

88 

164 

11 

3 

99 

167 

11.1 

1.8 

1951... 

212 

279 

10 

6 

222 

285 

4.5 

2.1 

1952... 

237 

353 

11 

16 

248 

369 

4.4 

4.3 

1953--- 

150 

278 

15 

13 

165 

291 

9.1 

4.5 

1954-.. 

195 

240 

17 

22 

212 

262 

8.0 

8.4 

1955.-. 

307 

267 

59 

44 

366 

311 

16.1 

14.1 

1956--- 

334 

449 

51 

105 

385 

554 

13.2 

19.0 

1957.-- 

251 

551 

79 

124 

330 

675 

23.9 

18.4 

1958-.- 

174 

195 

74 

59 

248 

254 

29.8 

23.2 

SOURCES : 


IKCES:  Commercial   landings    from   the   Oregon    Fish   Commission    Research    Laboratory   iii   Astoria,   Oregon. 
Sport  catch  estimates  from  Dr.  John  Rayner  of  the  Oregon  Game  Commission,   Portland,   Oregon. 
'  Columbia  River  sport  landings  have  been  equally  divided  between  Washington  and  Oregon  and  are  included  in 
part  herein. 


SPORT   CATCH    OP  OCEAN   SALMON 


295 


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FIGURE    1.      KING    (CHINOOK)    SALMON.      Numbers    of   ocean    caught   king    salmon    landed    by 
commercial  and  sport  fishermen  in  Washington,  Oregon,  and  California. 


296 


CALIFORNIA  FISH   AND  GAME 


The  percent  ocean  sport  catch  by  species  has  risen  from  over  4  in 
1952  to  nearly  30  in  1958  for  cliinook  salmon,  and  from  nearly  2  to 
over  23  for  silver  salmon  in  195U  and  1958  respectively.  JSilver  salmon 
contribnte  the  major  share  of  the  ocean  sport  catch  in  this  state,  aver- 
aging nearly  55  percent  from  1949  throngh  1958.  This  relationship 
holds  trnc  in  the  commercial  fishery  also. 

California 

Sport  fishing  for  salmon  in  California  occurs,  for  the  most  part, 
from  Monterey  Bay  northward.  Significant  catches  are  made  in  Mon- 
terey Bay,  otf  San  Francisco  Bay,  off  Fort  Bragg,  and  northward  from 
Eureka.  The  fishery  first  became  important  at  San  Francisco  which 
was  and  is  primarily  a  party  boat  fishery.  In  the  other  areas  the  pro- 
portion of  skiff  catches  is  much  higher.  (Total  landings  of  sport  and 
commercial  salmon  are  shown  in  Table  3  and  Figures  1  and  2.) 

The  ratio  of  king  to  silver  salmon  varies  from  port  to  port  and  sea- 
son to  season,  but  for  purposes  of  estimating  the  numbers  of  silver 
salmon  for  Table  3  it  was  assumed  that  the  relationship  found  in  1955 
and  1956  existed  from  1947  through  1958.  During  those  seasons  7.4 
percent  of  the  total  sport  landings  w^ere  silvers. 

Of  the  total  salmon  catch  in  California,  the  catch  by  the  ocean  sport 
fishery  has  ranged  from  less  than  1  percent  in  1947  to  a  high  of  22 
and  21  percent  in  1953  and  1955  for  chinook  and  silver  salmon  re- 
spectively. The  dramatic  increase  in  landings  which  occurred  in  1951 
has  fallen  off  in  1957  and  1958. 

KING  (Chinook)  SALMON 

The  chinook  catches  of  all  states  have  been  combined  to  indicate 
the  relative  strength  of  the  sport  catch  along  the  West  Coast  (Table 
4).  AVendler  and  Jnnge   (1957)   have  pointed  out  that  more  than  one 


TABLE  3 

California  Ocean  Sport  and  Commercial  Troll  Catches  in  Thousands  of  Fish  and 
Percent  Sport  Catch  1947  Through  1958 


Commercial  catcli 

Sport  catch 

Total  fish 

Percent  sport 

Year 

Cliinook 

Silvers 

Chinook 

Silvers 

Chinook 

Silvers 

Chinook 

Silvers 

1947--- 

610 

87 

5 

0.4 

615 

87.4 

0.8 

0.5 

1948.-- 

421 

93 

11 

1 

432 

94 

2.5 

1.1 

1949.-- 

400 

89 

23 

2 

423 

91 

5.4 

2.2 

1950--- 

430 

85 

57 

5 

487 

90 

11.7 

5.6 

1951--- 

416 

58 

103 

8 

519 

66 

19.8 

12.1 

1952--- 

474 

92 

123 

10 

597 

102 

20.6 

9.8 

1953--- 

490 

100 

141 

11 

631 

111 

22.3 

9.9 

1954--- 

771 

64 

171 

14 

942 

78 

18.2 

17.9 

1955..- 

747 

56 

184 

15 

931 

71 

19.8 

21.1 

1956.-- 

958 

68 

163 

13 

1,121 

81 

14.5 

16.0 

1957--- 

482 

89 

64 

5 

546 

94 

11.7 

5.3 

1958.-- 

350 

20 

65 

5 

415 

25 

15.7 

20.0 

SOURCE:  Salmon  and  steelhead  investigations.  Marine  Resouiees  Branch,   California  Department  of  Pish  and 
Game,  March  1959. 


SPORT    CATCH   OF   OCEAN   SALMON 


297 


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SILVER  SALMON  ,  OCEAN    LANDINGS 


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FIGURE  2.      SILVER  SALMON.      Numbers  of  ocean  caught  silver  salmon   landed   by  commercial 
and  sport  fishermen  In  Washington,  Oregon,  and  California. 


298 


(•.\lill''()KN'l.\    I'MSII    .\.\1)   (lAME 


A'car  class  ciilcrs  the  calch  of  both  ocean  li'oll  and  sport  lislicrics  in  a 
^'ivcn  year.  Hence,  a  inovinji'  avera^'c  c()inl)inin<i'  a1  least  two  years  was 
used,  not withstandinL;'  the  fact  that  the  sport  fisheries  ojx'i'ati'  on  two, 
three,  and  ])ossibly  four  year  classes. 

TABLE  4 

Washington,  Oregon,  and  California  Combined  Ocean  Ctiinook  Salmon  Catches  in  Thousands  of 

Fish  and  Percent  Catch  by  Fishery,  1947-1958 


CoMiinercial 
eatfh 

lOstiniated 
.sportr  catch 

Total 
landings 

Percent 

Combined  years 

Commercial 
landings 

Sport 
landings 

1947-48. 

1,642 
1,507 
1,575 
1,734 
2,077 
2,177 
2,409 
2,789 
3.02() 
2,679 
1,886 

28 
56 
124 
232 
373 
428 
461 
586 
659 
577 
468 

1,670 
1,563 
1,699 
1,966 
2,4,50 
2,605 
2,870 
3,375 
3,685 
3,2.56 
2,354 

98.3 
96.4 
92.7 
88.2 
84.8 
83.6 
83.9 
82.6 
82.1 
82.3 
80.1 

1.7 

1948-49     

3.6 

1949-50     .    -    

7.3 

1950-5 1 

11.8 

1951-52     .    

15.2 

19.52-,53 

16.4 

1 953-54 

1 954-55_ 

195.5-.56 

16.1 
17.4 
17.9 

1956-57     

17.7 

1957-58 

19.9 

Table  4  indicates  that  the  ocean  sport  catch  of  chinook  salmon  is 
approacliinii'  ^0  percent  of  the  total  catcli.  It  was  pointed  out  previously 
that  both  ()re«i()n  and  Washington  sport  catches  have  approached  or  ex- 
ceeded one-fourth  the  total  ocean  catch  in  these  states.  However,  Cali- 
fornia sport  catches  werc^  low  in  I!).")?  and  1!)58,  which  held  the  total 
percent  catch  for  all  states  combined  at  a  lower  level. 

SILVER  SALMON 

The  annual  catches  of  silver  salmon  ha\e  been  totaled  in  Tal)l(>  .").  Tn 
this  case  individual  years  have  been  used  since  the  j^'reat  majority  of 
the  silver  salmon  landed  are  in  their  third  year. 

TABLE  5 

Washington,  Oregon,  and  California  Combined  Ocean  Silver  Catch  in  Thousands  of 

Fish  and  Percent  Catch  by  Fishery,  1947  Through  1958 


Commercial 
catch 

Estimated 
sport  catch 

Total 
landings 

Percent 

Year 

Commercial 
landings 

Sport 
landings 

1947 

1948 

671 

839 

780 

800 

971 

1,288 

1,043 

707 

817 

1,223 

1.377 

740 

3.4 
4 

19 

21 

29 

56 

74 

99 
120 
258 
321 
209 

674.4 

843 

799 

821 
1,000 
1,344 
1,117 

806 

937 
1,481 
1,698 

949 

99.5 
99.5 
97.6 
97.4 
97.1 
95.8 
93.4 
87.7 
87.2 
82.6 
81.1 
78.0 

0.5 
0.5 

1949 --- 

2.4 

1950          

2.6 

1951 

1952 

2.9 
4.2 

1953 --- - 

6.6 

1954 

12.3 

1955 

12.8 

1956 

17.4 

1957 

18.9 

1958 

22.0 

SPORT   CATCH    OP   OCEAN   SALMON 


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FIGURE    3.      GROWTH    OF    THE    SPORT    FISHERY,      Combined    Washington,    Oregon,    and    Cali- 
fornia  sport  catches  of  ocean   caught  salmon   expressed   as   percent  of  the   total   ocean    landings. 
The  king  salmon  landings  have  been  smoothed  by  a  moving  average  of  two  years. 


300  CALIFORNIA  FISH   AND  GAME 

It  may  be  obsci'ved  that  llic  sport  catch  of  silvers  is  presently  ex- 
ceeding 20  percent  of  the  total  ocean  catch.  Prior  to  1953,  the  silver 
salmon  sjiort  catcli  was  Diiiior  in  almost  all  statics  when  <ir('ater  em- 
piuisis  was  placed  on  catcliiny  the  largei-  chinook  salmon.  However, 
with  the  advent  of  the  "mooching"  method  of  fishing  which  uses 
herring  for  bait,  and  the  earlier-season  fishing,  silver  salmon  were 
canght  in  largei-  numbers.  This,  coupled  with  greater  immbers  of  fisher- 
man trips,  makes  the  catch  of  this  species  by  sport  gear  an  important 
seofment  of  the  harvest. 


o^ 


SUMMARY  OF  COASTWISE  SPORT  CATCHES 

The  ocean  sport  catch  of  both  chinook  and  silver  salmon  has  increased 
phenomenally  over  the  past  10  years  and  is  presently  accounting  for 
over  20  percent  of  the  total  catcli.  There  is  some  indication  that  the 
percent  sport  catch  may  be  stabilizing  on  chinook  salmon.  The  sport 
fisherman  is  extending  his  season  in  time  and  is  tending  to  move  into 
the  area  that  normally  was  fished  only  by  the  commercial  troUer. 

LITERATURE  CITED 
Calhoun,  A.  J. 

19r)0.  California  angling  oateli  records  from  postal  card  surveys,  1936-1948,  with 
au   evaluation  of  postal   card   uonresponse.   Calif.   Fish   and   Came,    vol.   30, 
no.  3,  pp.  177-234. 
1951.  California  statewide  angling  catch  estimates  for  1949.  Calif.  Fish  and  Game, 

vol.  37,  no.  1,  pp.  69-75. 
1953.   Statewide  California  angling  estimates  for  1951.  Calif.  Fish  and  Game,  vol. 
39,  no.  1,  pp.  103-113. 

Kauffman,  Donald  E. 

1951.  Research  report  on  the  Washington  state  offshore  troll  fishery.  Bull.  I'ac. 
Mar.  Fish.  Conim.  2,  pp.  77-91. 

Pressey,  Richard  T. 

1953.  The  sport  fishery  for  salmon  on  Puget  Sound.  Wash.  Dept.  Fi.sh.  Res.  Pap., 
vol.  1,  no.  1,  pp.  33-48. 
Ryan,  James  H. 

1959.  Calif,  inland  angling  estimates  for  1954,  1956,  and  1957.  Calif.  Fish  and 
Game,  vol.  45,  no.  2,  pp.  93-109. 

Scofield,  W.  L. 

1956.  Trolling  gear  in  California.  Calif.  Dept.  Fish  and  Game,  Fish  Bull.  No.  103. 
Skinner,  John  E. 

1955.  California  statewide  angling  estimates  for  1953.  Calif.  Fish  and  Game,  vol. 
41,  no.  1,  pp.  19-32. 

Van  Hyning,  Jack  M. 

1951.  The  ocean  troll  fishery  in  Oregon.  Bull.  Pae.  Mar.  Fish.  Comm.  2,  pp.  43-76. 
Wendler,  Henry  O.  and  Charles  O.  Junge 

1957.  The  effect  of  the  ocean  sport  fishery  on  the  total  ocean  catch  of  chinook 
salmon  (Wash.  only).  Wash.  Dept.  Fish,  unpublished  report  on  file  at 
Seattle,  Wash. 

Washington  Dept.  of  Fisheries 

1956.  Columbia  River  Progress  Report,  August-December.  Unpublished  report  on 
file  at  Seattle,  Wash. 


TUNA  TAGGING  IN  THE  EASTERN  TROPICAL 
PACIFIC,   1952-1959^ 

C.  E.  BLUNT,  JR.  and  JAMES  D.  MESSERSMITH 

Marine  Resources  Operations 

California  Department  of  Fish  and  Game 

INTRODUCTION 

The  California  tuna  industry  is  the  most  important  fishery  industry 
in  the  state.  It  depends  primarily  upon  Pacific  yellowfin  tuna  (Neo 
fhimnus  macropterus)  and  skipjack  (Kaisuwonus^pelamis).  These  two 
compose  a  single  fishery  extending  from  California  to  Chile,  and  are 
exploited  by  large  tuna  clippers  and  purse  seiner-s  based  in  Southern 
California.  The  fishery  reached  an  all-time  high  in  productivity  in 
1950  when  over  150,000  tons  valued  at  over  45  million  dollars  to  the 
fishermen  were  landed.  Because  of  the  value  of  this  fishery  to  the  econ- 
omy of  the  State,  the  Department  of  Fish  and  Game  has  gathered  basic 
data  pertinent  to  its  management. 

One  of  the  fundamental  phases  of  any  fisliery  investigation  is  the  defi- 
nition of  the  stock  or  stocks  under  exploitation.  The  southerl}^  expansion 
of  the  tuna  fishery  into  northern  Peru  in  1950-51,  central  Peru  in  1953, 
and  northern  Chile  in  1957  has  increased  the  need  to  define  the  stocks 
that  support  the  industry.  Do  tlie  tuna  taken  from  these  areas  con- 
stitute a  single  stock  of  fish,  a  stock  that  does  not  intermingle  with  tuna 
from  important  fishing  areas  off  Central  America  and  Baja  California? 
Tagging  offers  the  most  direct  method  of  solving  this  problem. 

The  first  successful  method  of  tagging  tunas  Avas  de\eloped  by  in- 
vestigators of  the  California  Department  of  Fish  and  Came  in  1952. 
The  tags,  nev7  in  concept,  consisted  of  a  piece  of  polyvinylchloride 
plastic  tubing  looped  through  the  flesh  immediately  posterior  to  the 
second  dorsal  fins  and  were  developed  during  two  field  trials.  Results  of 
the  first  and  part  of  the  second  field  trial  Ave  re  summarized  by  Wilson 
(1953). 

His  report  described  in  detail  the  nine  tag  ideas  devised  for  the  first 
field  trial  and  the  three  tags  modified  from  them  for  use  in  the  second. 

Sinee  the  early  success  Avitli  ])lastic  tubing  the  California  "spaghetti" 
or  "loop  tag"  has  been  used  by  investigators  throughout  the  United 
States.  It  has  proven  quite  versatile,  and  in  Califoi'iiia  has  been  used 
successfully  on  several  species  of  salmon  (Oficorliy]icJnis  spp.),  steel- 
head  rainbow  trout  (Salmo  f/airdncri  (jairdneri),  California  yelloAvtail 
(Seriola  dorsalis),  kelp  bass  ( Paralahrax  clathratus),  California  halibut 
(Paralichthys  calif ornicus),  sturgeon  (Acipe'user  transmontanus  and  A. 
medirostris)  and  mauA'  others. 

1  Submitted  for  publication  January,  19G0. 

(301) 
3—17250 


302  CALIFORNIA  FISH  AND  GAME 

The  purpose  of  this  report  is  to  present  the  final  results  of  the  second 
field  trial  fi-om  October,  1952  through  April,  1954,  and  results  of  the 
regular  tuua  tagging  program  commencing  in  May,  1954  and  termi- 
nating ill  iMay,  1959.  Previous  to  our  initial  tagging  experiments, 
little  concrete  information  was  avaihible  concerning  migrations,  growth, 
and  po])ulatioii  units  of  tuna  that  sujiport  the  eastern  Pacific  fishery. 
Information  obtained  from  our  tagging  program  will  be  of  value  to 
other  governmental  agencies  investigating  them. 

THE  SECOND   FIELD  TRIAL 
Tags  Used 

Information  obtained  from  the  first  field  trial  was  used  in  the  de- 
velopment of  three  tags  (Types  E,  F,  and  G)  tested  during  the  second 
trial. 

Type  E  was  constructed  of  a  three-inch  piece  of  No.  20,  white,  XTE- 
30  Fibron  polyvinylchloride  tubing.  Upon  this  the  "return"  legend 
was  inscribed  in  black  vinylite  ink  manufactured  by  the  California 
Ink  Company,  Los  Angeles,  formula  number  104N5A2.  The  legend 
tubing  was  then  drawn  into  a  12-inch  piece  of  larger  tubing,  No.  14 
XTE-30  colored  transparent  Fibron.  A  piece  of  Type  302  stainless 
steel  wire  was  next  drawn  through  the  whole  unit  and  each  end  bent 
back  one-quarter  inch.  The  tubing  ends  Avere  then  heat-sealed  with  an 
electric  iron.  AVhen  applied  to  the  fish  the  ends  were  twisted  together 
(Figure  1). 

Type  F  w^as  similar  to  Type  E  except  that  27-pound-test  braided 
nylon  fishing  line  w^as  run  tlirough  the  assembly  in  place  of  the  stainless 
steel  wire.  The  ends  of  the  fishing  line  were  tied  in  a  square  knot  when 
applied  (Figure  1). 

Type  G  was  constructed  of  12-inch  lengths  of  No.  14  XTE-30  trans- 
parent Fibron  polyvinylchloride  tubing.  Through  this  was  run  a  19- 
inch  piece  of  No. '  20,  "white,  XTE-30  Fibron  tubing.  The  "return" 
legend  was  printed  on  the  center  of  the  inside  tubing.  To  secure  the  tag 
the  tubing  ends  were  tied  in  a  figure-eight  knot  drawn  tight  against 
the  ends  of  the  outside  jacket  and  neatly  trimmed  (Figure  1). 

Plastic  materials  for  all  three  tags  were  manufactured  by  the  Irv- 
ington  Varnish  and  Insulator  Company,  Irvington,  New  Jersey.  The 
outside  and  inside  diameters  of  their  No.  20  tubing  are  .066  and  .034 
inches  respectively.  Size  No.  14  tubing  is  .098  inches  outside  diameter 
and  .066  inside. 

Early  in  the  second  field  trial  evidence  began  to  accumulate  indi- 
cating that  Type  E  should  be  abandoned.  Difficulty  of  construction, 
bulkiness,  and  low  return  rate  all  combined  to  cause  its  removal 
from  the  field  trial.  We  felt  that  its  heavy  weight  W'Ould  cause  abrasion 
to  the  finlets ;  and  furthermore,  a  number  of  Type  E  tags  placed  on 
yellowtail  had  untwisted  (Collyer,  1954). 

Types  F  and  G  were  shortened  after  a  number  of  recoveries  during 
the  second  field  trial  made  it  increasingly  apparent  that  they  were  too 
long.  Type  F  was  shortened  to  nine  inches  and  the  outside  jacket  of 
Type  G  to  10  inches. 


TUNA    TAGGING 


303 


Techniques 

All  of  the  tags  used  in  the  second  field  trial  were  applied  l)y  means 
of  hypodermic-like  needles  made  from  stainless  steel  tubing.  Tlic  inside 
diameter  of  the  needle  was  such  that  the  end  of  the  tag  rode  secure 
inside  and  was  carried  through  the  flesli  when  the  neetlle  was  inserled 
into  the  fish.  After  removing  the  needle,  the  tag  was  pulled  through, 
centered,  and  the  ends  secured. 

TYPE      E 


TYPE      F 


TYPE      G 


FIGURE    1.      Tag  Types  E,  F,  and  G  used  in  the  second  field  trial. 


304  CALIFORNIA  FISH   AND  GAME 

One  of  the  major  jn-obloms  inherent  in  tagging  tunas  is  to  remove 
the  fisli  from  the  -water  and  affix  the  tag  and  return  it  to  the  water 
before  a  death  spasm  takes  place,  liesults  of  the  first  field  trial  demon- 
strated that  with  careful  methods  some  of  the  tunas  would  survive.  All 
initial  work  was  done  aboard  the  department's  research  vessel  N.  B. 
SCO  FIELD  where  sufficient  help,  space  and  facilities  were  available 
for  experimentation.  During  the  second  field  trial  much  of  the  tagging 
was  done  aboard  commercial  tuna  clippers,  a  very  satisfactory  and  eco- 
nomical method  because  of  the  fine  cooperation  received. 

We  had  found  from  experience  that  at  least  two  men  are  needed  to 
tag  tuna  etficientlj'  aboard  commercial  clippers.  The  tagger  and  his 
sponge-rubber-lined  tagging  cradle  should  be  located  near  the  stern  on 
the  starboard  side  away  from  the  fishermen  in  the  racks  on  the  port  side. 
The  second  man  usually  fishes  from  one  of  the  stern  racks  and  is  able  to 
swing  fish  gently  around  to  the  tagger.  The  tagger  then  quickly 
affixes  the  tag,  measures  the  fork  length  of  the  fish  and  releases  it  into 
the  water.  Records  are  kept  on  plastic  sheets  on  which  tag  numbers 
were  entered  in  advance. 

Results 

During  the  second  field  trial  4,204  yellowfin  tuna  and  2,839  skip- 
jack were  tagged  (Table  1)  throughout  the  tropical  commercial  fishing 
area,  with  the  majority  released  off  Baja  California  and  South  America. 
Attempts  were  made  to  test  tag  Types  F  and  G  by  tagging  in  alternate 
lots  of  from  5  to  15  tags  each.  Because  of  numerous  problems  encoun- 
tered in  tagging  at  sea  and  poor  availability  of  materials,  it  was  not 
possible  to  alternate  types  completely  until  the  latter  part  of  the  trial. 

In  order  to  compare  recovery  rates  of  Type  F  and  G  tags,  the  data 
used  in  Table  1  were  resnmmarized  to  include  only  those  cruises  on 
which  both  types  were  used  (Table  2).  Recoveries  favored  the  Type 
G  tag  for  both  yellowfin  tuna  and  skipjack.  A  Chi-square  test  showed 
significant  differences  in  returns  for  both  vellowfin  tuna  and  skip- 
jack  (P<. 05). 

The  apparent  superiority  of  the  Type  G  tag,  as  used  in  the  second 
field  trial,  was  probably  due  more  to  its  greater  visibility  than  to  basic 
structural  ditferences,  since  Type  F  tags  have  held  secure  on  alba- 
core  migrating  across  the  Pacific  during  periods  of  liberty  up  to  325 
days  (Ganssle  and  Clemens,  1953,  Blunt,  1954).  Most  of  the  Type  F 
tags  used  during  the  second  trial  had  to  be  constructed  of  clear  poly- 
vinylchloride  tubing,  (the  only  material  available)  giving  them  a  lower 
A'isibility  factor  than  the  Avliite  Type  G. 

On  the  basis  of  the  second  field  trial  Type  G  was  selected  as  the 
most  efficient  and  a  full-scale  tagging  program  was  undertaken. 

MODIFICATIONS  AND  EXPERIMENTS  SINCE  SECOND  FIELD  TRIAL 

Material 
Mar/c/ng  Ink  and  Tag  Construcfion 

Previous  to  our  initial  tagging  experiments  in  1952,  an  ink  satis- 
factory for  marking  vinylite  plastic  had  not  been  formulated.  With  the 
manufacture  of  vinylite  ink.  Formula  104N5A2,  it  was  possible  to 
inscribe  an  apparently  resistant  legend  and  number  on  each  tag.  The 


TUNA    TAGGING 


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306  CALIFORNIA  FISH  AND  GAME 

TABLE  2 
Releases  and  Recoveries  During  Second  Field  Trial  Using  Type  F  and  G  Tags 


Yellowfin  Tuna 

Skipjack 

Tagged 

Recovered 

Tagged 

Recovered 

Tag  type 

Number 

Number 

Percent 

Number 

Number 

Percent 

F 

G 

1,844 
1,799 

9 
23 

0.49 
1.28 

1,335 
1,309 

7 
18 

0.52 
1.38 

legend  proved  adequate  when  protected  by  a  transparent  outer  jacket 
and  placed  at  the  center  of  the  tubing  (that  part  embedded  in  the 
fish)   to  prevent  fading. 

MidAvay  through  the  regular  tagging  program  it  was  felt  that  re- 
moval of  the  jacket  from  Type  G  tags  would  simplify  them  and  in- 
crease tagging  speed.  This  Avas  done  in  1956  (Cruise  56S1  Table  6) 
when  an  ink.  Formula  10-1:N5A4,  considerably  more  resistant  to  light, 
became  available. 

Plastic  Tubing 

Shortly  after  the  onset  of  the  regular  tagging  program  it  became 
evident  that  the  viuylite  in  recovered  tags  had  lost  some  of  its  flexi- 
bility. Manufacturers  indicated  that  this  probabh'  was  caused  by  the 
leaching  out  of  the  plasticizer,  the  chemical  component  in  viuylite 
responsible  for  softness  and  flexibility.  This  partial  loss  of  flexibility, 
however,  did  not  appear  to  have  affected  the  efficiency  of  the  tags. 
Examination  of  numerous  tags  on  fish  that  had  been  at  liberty  for 
periods  between  one  and  two  years,  indicated  the  material  definitely 
was  not  brittle,  and  still  retained  satisfactoiy  flexibility. 

Experience  with  yellow  viuylite  tags  during  the  early  part  of  the 
program  indicated  the  color  faded  considerably,  even  while  on  fish  at 
liberty  for  periods  shorter  than  three  months.  In  1957,  an  improved 
yellow,  Resinite  X-270-I  (viuylite),  was  put  on  the  market  by  the 
Borden  Company  of  Santa  Barbara,  California.  This  material  was 
somewhat  similar  to  XTE-30  but  Avas  considerably  softer  and  had  been 
formulated  to  retain  flexibility  longer.  Starting  in  November  1957,  all 
tags  Avere  manufactured  Avith  it. 

Methods 

Tagging  techniques  used  during  the  regular  program  basically  Avere 
similar  to  those  used  during  the  second  field  trial  (Wilson,  1953).  A 
rather  important  innovation  in  1954  Avas  the  placing  of  a  wet  burlap 
sack  or  cloth  over  the  fish's  head  to  aid  in  quieting  it  during  the 
tagging. 

Tagging  needles  also  Avere  modified  slightly.  During  the  second  field 
trial  a  needle  of  stainless  steel  tubing  Avitli  the  end  ground  to  a  sharp 
hypodermic-like  point  was  used  to  insert  the  tag  in  the  fish.  The  sharp 
edges  of  this  needle  cut  as  it  pierced  the  flesh.   To  alleviate  this,  a 


TUNA    TAGGING 


:}07 


stainless  steel  rod  was  forced  into  one  end  of  the  steel  tube  and  then 
ground  to  a  sharp  rounded  point.  This  solid-point  needle  eliminated 
much  of  the  cutting  of  tissue  during  tagging  and  resulted  in  reduced 
bleeding. 

Detection  of  Tagged  Fish 

To  publicize  the  tagging  program  posters  in  Spanish  and  English 
were  distributed  throughout  the  fishing  ports  and  canneries  of  the 
United  States,  Mexico,  and  Central  and  South  America. 

The  natnre  of  the  fishery  is  such  that  individual  tuna  are  handled 
at  least  once  before  being  weighed  at  the  cannery,  after  which  there 
is  at  least  one  additional  handling  before  cooking  and  canning.  Be- 
tween the  actual  removal  of  the  tuna  from  the  sea  by  the  fishermen 
and  this  final  process  there  are  numerous  additional  instances  where 
tagged  fish  could  be  detected  by  both  fishermen  and  cannery  personnel. 
Fishermen  often  notice  tagged  fish  lying  on  deck  before  they  are 
passed  into  the  refrigerated  wells  for  storage.  Cannery  personnel  also 
liave  returned  tags  to  us  that  were  first  observed  on  fish  on  a  con- 
veyor in  transit  to  the  cutting  and  cleaning  line. 

Despite  these  many  opportunities  for  recovering  tagged  fisli  it  be- 
came evident  early  in  the  program  that  a  substantial  number  of  tags 
were  not  being  detected  and  thus  were  lost.  Fishermen  reported  nu- 
merous sightings  of  tagged  fish,  but  due  to  the  arduous  and  often 
hurried  working  conditions  aboard  tuna  vessels  many  were  never  re- 
covered— even  when  personnel  were  assigned  to  look  for  them  during 
unloading  at  the  cannery.  Unknowni  to  crew  members,  tagging  per- 
sonnel "salted"  16  tagged  fish  in  selected  storage  wells.  Of  these  16, 
only  six  were  subsequently  recovered;  four  by  cannery  personnel,  and 
two  by  fishermen.  The  other  10  were  never  seen  again.  These  findings 
indicated  a  high  tag  loss  during  handling  and  processing,  but  it  prob- 
ably would  have  been  even  higher  had  we  not  used  some  yellow  tags 
(Table  3).  The  better  recovery  rate  for  yellow  tags  is  likely  due  to 
the  better  visibility  of  this  color  (Lahr  et  at.,  1959). 

f^\e\6  Testing 

Experiments  testing  the  visibility  of  different  colors  were  conducted 
in  1956  and  1957.  Alternating  lots  (five  each)  of  red,  white,  and  bine 
tags  were  released  (Table  4).  There  was  no  indication  that  red  or  blue 
gave  improved  returns  over  the  standard  white  tag. 


TABLE  3 
Recoveries  of  Tagged  Tuna  Planted  in  Storage  Wells  at  Sea 


Tag  color 

No.  planted 

No.  recovered 

No.  lost 

Red                         

3 

7 
1 
5 

1 
1 
0 
4 

2 

White                             -- 

6 

Blue                                    -   

1 

YeUow 

1 

Totals                    -- 

16 

6 

10 

308 


CALIFORNIA  FISH  AND  GAME 

TABLE  4 

Releases  and  Recoveries  of  Tuna  Tagged  During  an  Experiment  Using 
Red,  White,  and  Blue  Tags 


Red  tags 

White  tags 

Blue  tags 

Cruisei 

Tagged 

Recovered 

Tagged 

Recovered 

Tagged 

Recovered 

56C3 

224 
263 
304 
200 
273 

5 

2 
1 

1 
1 

218 
265 
304 
201 
257 

1 
3 

2 
1 
2 

219 
265 
302 
196 
94 

3 

56C4 

56C5 

57C1 

57C4 

3 
5 

1 
0 

Totals 

1,264 

10 

1,245 

9 

1,076 

12 

1  See  Table  6. 

Dart  Tag  Experiments 

Since  the  early  stages  of  the  program  dart-type  tags  had  been  seri- 
ously considered  because  of  their  simplicity  and  speed  and  ease  of 
application.  It  was  not  until  late  1955,  however,  that  we  were  able  to 
test  them.  During  an  exploratory  oceanographie  and  longline  fishing 
cruise  (No.  55S5),  as  a  part  of  expedition  Eastropic,  a  total  of  72 
yellowfin,  skipjack,  and  bigeye  tuna  was  tagged  alternately  with  dart 
and  Type  G  "spaghetti"  tags.  There  were  no  recoveries  from  these, 
probably  due  to  the  fact  the  fish  were  caught  on  trolling  lines  and 
released  throughout  a  very  large  area  in  the  eastern  tropical  Pacific. 
The  dart  tags  had  been  obtained  through  the  courtesy  of  the  Woods 
Hole  Oceanographie  Institution.  Dart  tags  of  various  other  types  were 
used  in  limited  quantities  in  1957  and  1958  but  none  M^as  recovered. 

Yamashita  and  Waldron  (1958)  reported  good  results  from  an  all- 
plastic  dart  tag  used  in  Hawaiian  waters  in  1957.  Recovery  rates  up 
to  13  percent  were  realized  from  two  lots  of  about  5,000  skipjack. 

In  early  1959,  we  field  tested  a  FT-2  dart  tag  manufactured  by  the 
Ploy  Tag  Company  of  Seattle,  Washington.  It  has  a  solid  dart  head 
one  inch  long  constructed  of  Zytel  nylon.  Attached  to  this  is  a  six-inch 
piece  of  No.  18,  EP-2,  yellow  vinylite  tubing  manufactured  by  the 
Borden  Company  of  Santa  Barbara,  California  (Figure  2). 

Both  yellowfin  and  skipjack  were  tagged  alternately  with  FT-2  dart 
tags  and  Type  G  "spaghetti"  tags  off  the  coasts  of  Peru  and  Central 
America  during  Cruise  59C1  (Table  5).  The  dart  tag  was  applied  to 
the  fish  with  a  hollow  stainless  steel  needle.  They  were  pushed  about 
one  inch  into  the  flesh  near  the  posterior  portion  of  the  second  dorsal 
fin  base.  Skipjack  recoveries  were  overwhelmingly  in  favor  of  the  dart 
tag.  Since  the  tag  types  were  released  alternately  it  is  believed  the  dif- 
ferences in  recovery  rates  indicate  a  lower  tagging  mortality  resulting 
from  the  dart  tag.  No  yellowfin  were  recovered. 

TAGGING  RESULTS 
Areas  of  Tagging 
Due  to  the  vagaries  of  fishing  it  was  not  possible  to  release  tags  in 
selected  areas.  In  general,  however,  the  areas  exploited  by  tuna  fisher- 
men go  hand-in-hand  with  the  seasons  of  the  year.  During  winter,  most 


TUNA    TAGGING 


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310  CALIFORNIA  FISH   AND  GAME 

fishing  is  conducted  in  the  vicinitj^  of  the  Galapagos  Islands  and  off 
Central  and  South  America.  In  the  spring,  fishing  increases  off  Central 
America  and  ]\Iexico  and  by  summer  the  fleet  concentrates  off  Baja 
California.  In  recent  years,  substantial  tonnages  of  yellowfin  and  skip- 
jack have  been  taken  during  all  months  off  Baja  California. 

Some  yellowfin  and  skipjack  were  tagged  and  released  from  tuna 
clippers  in  all  of  the  major  fishing  areas  except  the  Gulf  of  California. 
The  Gulf  of  C*alifornia  produces  good  catches  of  relatively  large  yellow- 
fin tuna,  but  they  have  traditionally  been  exploited  more  efficiently  by 
the  purse  seine  fleet.  Due  to  the  limited  and  sporadic  fishing  in  the 
vicinities  of  Clipperton,  Cocos  and  Malpelo  Islands  tew  tags  were  re- 
leased at  these  locations. 

Though  cooperation  of  the  tuna  fleet  was  excellent  during  the  pro- 
gram, scheduling  of  tagging  trips  was  hindered  by  labor  strikes,  tieup 
of  vessels  for  economic  reasons,  inability  of  small  clippers  to  take  two 
extra  men  and  a  shortage  of  tagging  personnel.  Despite  these  hin- 
drances an  average  of  four  tagging  trips  was  taken  aboard  commercial 
vessels  each  year.  Additional  tuna  tagging  w^as  conducted  aboard  the 
research  vessel  N.  B.  SCOFIELD  in  conjunction  with  albacore  and 
.yellowtail  w^ork.  The  39  tagging  trips  since  the  inception  of  the  program 
are  listed  in  Table  6. 

During  both  the  experimental  phases  and  our  regular  tagging  pro- 
gram 27,478  yellowfin  tuna  and  skipjack  were  tagged  in  the  eastern 
tropical  Pacific.  To  show  these  diagramatically,  the  number  of  fish 
tagged  and  released  in  each  one-degree  square  has  been  listed  on  the 
three  charts  covering  the  range  of  the  fishery  (Figures  3a,  b,  c  and  4a, 
b,  c).  The  number  of  recoveries,  through  November  30,  1959,  from  fish 
tagged  in  each  one-degree  square  has  been  entered  above  the  number 
tagged.  Detailed  information  concerning  month  and  year  of  tagging 
and  recovery  is  presented  in  Appendices  A,  B,  C  and  D. 


■ty. 


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SOLID      ZYTEL      NYLON 

FIGURE   2.      Type  FT-2  dart  tag. 


TUNA    TAGGING 


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number   tagged.    Recoveries    were    not    necessarily    made    v/ithin    the    degree    square    of    tagging. 


314 


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TUNA    TAGGING 


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Galapagos   Islands.  The    number  recovered   from  each    lot  is  indicated   over  the   number  tagged. 

Recoveries  were  not  necessarily  made  within  the  degree  square  of  tagging. 


TUNA    TAGGING  319 

Recoveries  of  Tagged  Yellowfin  Tuna 

Through  November  3U,  1!)5!),  203  of  13,213  tagged  j^eHowfin  tuna 
were  returned.  They  had  been  at  liberty  from  one  to  842  days  and 
demonstrated  straight  line  movements  up  to  1,025  miles.  To  represent 
pictorially  a  summary  of  tagged  yellowfin  movements  by  periods  of  the 
year,  fish  recovered  75  or  more  miles  from  point  of  tagging  were  jilof- 
ted  on  charts  encompassing  the  range  of  the  eastern  I'aeifie  tunas  (Fig- 
ures 5,  6,  and  7).  Detailed  information  for  every  recovery  can  be 
found  in  the  appendices. 

At  the  northern  extremity  of  tlie  fishery  all  of  the  within-season 
recoveries  of  fish  tagged  during  May  demonstrated  a  definite  north- 
ward movement.  Two  even  moved  from  the  Revilla  Gigedo  Islands  to 
Baja  California  (Figure  5a).  One  of  the  off-season  recoveries  (January- 
April)  was  captured  in  the  Gulf  of  California.  Recoveries  of  fish  tagged 
during  June  indicated  northerly  movements,  with  one  migrating  from 
the  Revilla  Gigedo  Islands  to  the  mainland  of  Baja  California  (Figure 
5b).  Most  of  the  fish  tagged  during  July  also  moved  north  with  oidy 
four  moving  south  (Figure  5c).  Of  those  moving  south,  one  traveled 
from  Baja  California  to  the  Revilla  Gigedo  Islands.  Fish  tagged  during 
September  and  October  moved  southward  (Figure  5d). 

Movements  of  tuna  tagged  off  Mexico  and  Central  America  were 
considerably  more  spectacular  in  that  several  traveled  straight  line 
distances  greater  than  1, ()()()  miles  (Figure  6a).  All  recoveries  of  fish 
tagged  in  these  areas  during  February,  March  and  April  dcnionstrated 
northerly  migrations.  An  important  feature  is  the  movement  of  four 
yelh)wfin  tuna  from  the  vicinity  of  the  Gulf  of  Tehuantepec  to  the  Gulf 
of  California,  Baja  California  and  the  Revilla  Gigedo  Islands.  These 
four  were  tagged  in  February  within  a  few  miles  of  each  other;  1lie 
first  was  recovered  in  the  Gulf  of  California  in  May,  the  second  off 
Baja  California  in  August,  and  the  third  and  fourth  near  the  Revilla 
Gigedo  Islands  in  October  and  November.  Other  significant  i-ccoveries 
were  two  fish  tagged  off  Central  America  which  crossed  the  (!ull'  of 
Tehuantepec  and  were  recaptured  off  Mexico.  Recoveries  of  fisii  tagged 
in  June  and  December  appear  in  Figure  6b.  One  fish  tagged  in  June 
was  of  particular  significance  in  that  it  demonstrated  evidence  of  a 
migration  between  the  Mexican  mainland  and  an  offshore  island.  The 
best  information  available  from  the  recovery  vessel  indicates  it  ])roba- 
bly  was  caught  at  Clipperton  Island,  but  there  is  a  slight  i)()ssibility  it 
was  caught  at  New  Clarion  Bank  near  the  Revilla  Gigedo  Islands. 

A  yellowfin  tagged  north  of  the  Galapagos  Islands  in  March  moved 
to  the  Gulf  of  Guayaquil  (Figure  7a),  and  two  tagged  in  October  in 
the  vicinity  of  the  Gulf  of  Guayaquil  moved  south  to  centi'al  Per-n. 
Those  tagged  during  November  and  Decend^er  indicated  an  intei-change 
between  the  Gulf  of  Guayaquil  and  the  14  Fathom  Bank  off  INmii 
(Figure  7b). 

D'scussion 

From  the  Baja  California  tag  returns  we  infer  that  yellowfin  tuna 
move  north  along  the  coast  of  Baja  California  dui'ing  May,  June  and 
July.  During  the  latter  month  some  start  to  move  south,  and  southerly 
movements  continue  through  September  and  October.  Also  there  is  an 


:{2() 


rALIFORXIA    FTSll    AND   OAME 


FIGURE   5a.      Yellowfin    tuna    movements    of   75    or    more    miles    as    shown    by    recoveries    of    fish 
tagged  in  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


interchange  of  yellowfin  between  Baja  California  and  the  Revilla 
Gigedo  Islands.  Further  the  seasonal  fisheries  off  Baja  California,  the 
Gulf  of  California,  and  the  Revilla  Gigedo  Islands  are  supported  in 
some  degree  by  the  northerly  movements  of  yellowfin  tuna  along  the 
Mexican  coast  in  winter  and  spring  from  at  least  as  far  south  as  the 
Gulf  of  Tehuantepec.  Recoveries  of  two  fish  tagged  off  Central  America 
that  crossed  the  Gulf  of  Tehuantepec  to  central  Mexico  bring  out  the 


TUNA    TAGGING 


321 


possibility  tliat  in  some  years  fish   from   Ccmtral    Aincrira    iiia\    iiioxe 
into  these  fishing  areas. 

Recoveries  at  various  localities  of  four  j^ellowfin,  tagged  in  February 
within  a  few  miles  of  each  other  near  the  Gulf  of  Tehuantepec,  may 
indicate  that  the  schools  into  which  they  were  released  first  entered  the 
Gulf  of  California  around  May,  moved  to  the  Baja  California  fishing 
grounds  by  August  and  then  traveled  to  the  Revilla  Gigedo  Islands  in 
October  and  November   (Figure  6a). 


FIGURE   5b.      Yellowfin    tuna    movements    of   75    or    more    miles    as    shown    by    recoveries    of    fish 
tagged  in  1953  and  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


CjOO 


(  Al.lFOKNIA   FlSir    AND   GAME 


FIGURE   5c.      Yellowfin    tuna    movements   of   75    or    more    miles   as   shown    by    recoveries   of   fish 
tagged  in  1953,  1956,  and  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


The  Baja  California  fishery  is  exploited  effectively  by  purse  seiners 
and  baitboats  during  late  spring,  summer  and  fall  and  substantial  ton- 
nages are  caught.  When  the  fishery  fails,  generally  by  winter,  the  area 
or  areas  to  which  these  fish  disseminate  are  in  question.  Since  there 
were  no  recoveries  of  Baja  California  tagged  fish  along  the  Mexican 
coast  it  appears  there  was  little  or  no  movement  in  that  direction.  Tag 
returns  did  indicate  some  dissemination  of  fish  from  Baja  California 
to  the  Gulf  of  California. 


TUNA    TAGGING 


323 


FIGURE   5d.      Yellowfin    tuna    movements    of    75    or    more    miles    as    shown    by    recoveries    of    fish 
tagged  in   1952  and  1955.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


324 


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CALIFORNIA  FISH   AND  GAME 


Substantial  numbers  of  recoveries  of  fish  tagged  off  Baja  California 
have  been  made  the  following  season  (Table  7),  many  within  90  miles 
of  the  point  of  tagging.  One  tnna  tagged  in  July  1956  Avas  recaptured 
842  days  later  only  87  miles  from  its  release  point.  The  small  number 
of  off-season  recoveries  reflects  their  virtual  disappearance  during  that 
period  of  the  year.  This  suggests  the  possibility  that  Baja  California 
tuna  migrate  to  areas  not  subjected  to  fishing  at  that  time  of  year. 


TABLE  7 

Season  of  Recapture  for  167  Yellowfin  Tuna  Tagged,  May  to  December,  Off 
Baja  California,  1952-1958 


Within-season  (May  to  Dec.) 

Off-season 
(Jan.  to  Apr.) 

Within-season 
(One  year  later) 

Within-season 
(Two  years  later) 

150 

4 

12 

1 

Fish  tagged  off  the  Gulf  of  Guayaquil  and  Peru  did  not  move  from 
these  areas  into  Central  America  (Figure  7a,  b).  Movement  between 
the  Galapagos  Islands  and  the  Gulf  of  Guayaquil  does  take  place  as 
evidenced  by  one  recovery.  Recoveries  made  along  the  coast  of  Peru 
indicate  that  there  is  some  movement  between  the  Gulf  of  Guayaquil 
and  the  14-Fathom  Bank  throughout  the  year. 


COCOS       IS 


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TAGGED  IN        MARCH -OCT- 
LEGEND 
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TAGGED      IN      MARCH 

--     TAGGED        IN      SEPT. 

TAGGED        IN      OCT 

DIRECTION      OF     MOVEMENT 


FIGURE  Ta.      Yellowfin   tuna    movements   of   15   or    more   miles   as   stiown    by   recoveries   of   fish 
tagged  in  1954  and  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


TUNA    TAGGING 


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FiGURE   7b.      Yellowfin    tuna    movements    of    75    or    more    miles    as    shown    by    recoveries    of    fish 
tagged  in  1952  and  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 

Tao'g'ing  mortality  and  nonobservation  of  tags  during  normal 
liandling  and  processing  of  the  tnnas  have,  without  doubt,  materially 
affected  the  recovery  rates.  Even  so  recoveries  of  tagged  yellowfin 
tuna  from  1954  to  1959  indicate  a  rate  of  harvest  which  in  most  areas 
would  not  be  expected  to  have  an  appreciable  effect  upon  the  popula- 
tion (Table  8).  Exceptions  might  be  the  Baja  California  and  Peruvian 
fisheries. 


TABLE  8 
Recovery  Rates  of  Yellowfin  Tuna  Tagged  in  Ten  Fishing  Areas,  May,  1 954  fo  May,  1 959 


Fishing  area 

No.  tagged 

No.  recovered 

Percent  returned 

Baja  California 

Revilla  Gigedo  Islands 

Coast  of  Mexico 

Central  America 

Clipperton  Island        -    -    - 

1,845 

421 

2,321 

2,412 

54 

76 
330 

51 
1,078 

70 

150 
7 
8 
6 
0 
0 
1 
0 
48 
0 

8.1 
1.7 
0.3 
0.2 
0 

Cocos  Island 

Galapagos  Islands 

Ecuador-Columbia 

Guayaquil-Peru..    -_    

0 

0.3 

0 

4.5 

ChUe   

0 

328 


(■  \I,IK(IK'\1  A     I'lSII     A  \I)    (;A  M  I') 


Sliiiii;iil;i  :iii(l  Scli.-id'cr  (IDHf))  sliidicd  llic  rcl;il  ioiisli  i  p  liclwccii 
|)()|)iil:il  ion  .•ihiiii(l;i  lire  .ind  lisliiii^  iiitciisily  in  llic  ciislci-ii  l*;i('ili('  Tor 
the  ycni's  II'MI  lo  ll'.').",.  Tliry  coiicliKlcd  lli;M  (isliiii!^'  Ii;is  liiid  ;i  fc;d 
cd'ccl  ii|t()ii  llic  stock  (>r  c;is|cni  I'aciCic  _yc|]o\vlhi  liiiKi,  l;ikcii  in  llie 
tifjffjreji'Jil c,   (i\('r   llic    pci'iod   sliidicd. 

l\;illicr  l;ir^'c  dinVrciiccs  in  rccoxcry  rates  exis1  hclwccii  llic  cciilcr 
()!'  the  lisliiiiij:  raiij^rc  oil"  Mexico,  Cciilral  ATnci'ica,  l^^ciiador-Colotiihia 
and  areas  near  the  iiorllicni  and  soiillicni  cxlrcniies  olT  I'.aja  Calil'ornia, 
and  Guayaciuil-Peru.  Tag  rc<M)vcrics   Irom    r>aja   ( "aiirornia  and    I'crn- 


120' 


I         I 


no* 

~i — 


30 


25 


20 


ADALUPE       IS. 

0 


SKIPJACK         MOVEMENTS 
TAOOEO      IN      MAY 

LEGEND 
WITHIN       SEASON      RECOVERIES 
OVEMENT 


30 


-25 


20 


REVILLA        GIGEDO       IS. 


120* 


-L         1  I  i: 


15* 


I  1 


no* 


FIGURE   8a.      Skipjack    movements   of  75  or   more    miles   as   shown    by    recoveries   of  fish    tagged 
in  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


TUNA    TAGGING  329 

Guayaquil  were  8.1  aud  4.5  percent  respectively.  Tagging  in  the  cen- 
tral areas  of  the  fishery  yielded  between  0.2  and  0.8  percent. 

The  reasons  for  these  differences,  which  are  considerably  more  diver- 
gent than  would  be  expected,  are  not  readily  apparent. 

Recoveries  of  Tagged  Skipjack 

Through  Xovcmbci'  v'.ii.  lli.l!).  237  of  14,26o  tagged  skipjack  bad  been 
received.  They  had  been  at  liberty  from  one  to  271  days  and  demon- 
strated straight  line  movements  of  up  to  720  miles.  Those  having 
moved  75  or  more  miles  were  selected  for  graphic  presentation  (Fig- 
ures 8,  9,  and  10  j.  Detailed  information  for  every  recovery  can  be 
found  in  the  Appendices. 

Baja  California  and  the  Revilla  Gigedo  Islands  movements  (Figures 
8a,  8b,  8e,  8d)  were  by  fish  that  had  been  at  liberty  from  8  to  139 
days  and  traveled  80  to  410  miles.  Fish  tagged  in  these  areas  in  .M;i\- 
'Figure  8a)  geuprally  mo\i'(i  iifjr-ofi'^t.  one  goinir  from  Roca  Partida. 
Revilla  Gigedo  Islands,  to  liaja  <'rilifornia.  Thi>,  nottlierly  movement 
was  also  demonstrated  by  some  of  tin-  June  tagging  returns  ('Figure 
8b).  Returns  from  July  tagging  C Figure  8c j  demonstrated  a  predomi- 
nant northerly  movement,  extending  to  the  California-Mf^xir-o  border: 
however,  one-third  were  recovered  south  of  the  tagging  point.  All 
recoveries  from  September  tagging  showed  a  southerly  movement 
(Figure  8d). 

<")nly  three  returns  were  received  ffom  tagging  off  Mexico  and  Cen- 
tial  America  ('Figure  9),  two  of  wliidi  had  moved  more  than  75  miles. 
Both  were  recovered  north  of  the  point  of  tagging. 

Movements  shown  in  Figures  10a.  b,  and  e  for  Ecuador  and  Peru 
were  from  fish  that  had  been  at  liberty  from  16  to  192  days,  and  had 
moved  75  to  120  milHs.  April  tagging  returns  from  this  area  ('Figure 
10a j  demonstrated  northerly  movement  from  tin-  14-Fathom  Bank  to 
the  Gulf  of  Guayaquil  and  Ecuador.  September  and  October  tagging 
Figure  lObj  showed  an  interchange  of  fish  between  the  14-Fathom 
Bank  and  the  Gulf  of  Guayaquil,  with  one  fish  moving  from  the  Gulf 
of  Guayaquil  to  an  area  north  of  the  Galapagos  Islands.  November, 
December  and  January  tagging  returns  ('Figure  10c)  showed  several 
movements  to  the  Gulf  of  Guayaquil  from  the  14-Fathorn  Bank,  and 
one  to  the  14-Fathom  Bank  from  tlK'  (lulf  of  Guayaquil. 

Discussion 

Returns  from  tagging  off  Baja  California  indicate  a  northerly-  move- 
ment in  May  and  June  ("Figure  8a,  b)  ;  a  tran.sitional  period  with 
movements  both  north  and  south  during  July  (Figure  8c)  and  an 
'■ntirely  .southerly  movement  in  September  ("Figure  8d).  Movement 
between  the  Revilla  Gigedo  Islands  and  Baja  California  was  evidenced 
by  a  single  recovery  off  Baja  California. 

Returns  from  tagging  off  Ecuador  and  Peru  revealed  a  general  inter- 
change of  fish  between  the  14-Fathom  Bank  and  the  Gulf  of  Guayaquil 
(Figures  10b.  c).  Returns  from  tagging  during  April  CFigure  10a) 
demonstrated  a  movement  from  the  14-Fathom  Bank  to  the  Gulf  of 
Guayaquil. 

A  skipjack  tagged  in  October  near  the  Gulf  of  Guayaquil  and  re- 
covered 45  days  later  north  of  the  Galapagos  I.slands  indicated  a  move- 
ment between'  the  mainland  and  the  Galapagos  Islands. 


330 


CALIFORNIA  FISH    AND  GAME 


FIGURE   8b.      Skipjack    movements   of  75   or    more   miles   as  shown    by    recoveries  of  fish   tagged 
in  1953  and   1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


TUNA    TAGGING 


331 


120° 


30 


25 


20 


GUADALUPE         IS 


30 


20 


V  I 


REVILLA         GIGEDO        IS, 


I  I 


120° 


115° 


10° 


FIGURE   8c.      Skipjack    movements   of  75    or    more   miles   as  shown    by   recoveries   of  fish    tagged 
in  1953,  1956,  and  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


332 


CALIFORNIA  FISH  AND  GAME 


K  I 


120° 


110° 

~i — 


30 


25 


20 


GUADALUPE  IS. 


PJACK  MOVEMENTS 

ED  IN       SEPTEMBER 


30 


20 


REVILLA         GIGEDO        IS 


120° 


110° 


FIGURE   8d.      Skipjack   movements  of  75   or   more   miles  as  shown   by   recoveries  of  fish  tagged 
in  1955.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


TUNA    TAGGING 


333 


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SKIPJACK  MOVEMENTS 

TAGGED  IN        APRIL 

LEGEND 
WITHIN  SEASON  RECOVERIES 

DIRECTION        OF        MOVEMENT 


III'  ^1 


FIGURE    10a.      Skipjack   movements  of  75  or  more   miles  as  shown  by  recoveries  of  fish  tagged 
in  1959.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


COLOMBIA 


SKIPJACK         MOVEMENTS 
TAGGED        IN       SEPT  -  OCT 

LEGEND 
WITHIN         SEASON         RECOVERIES 
DIRECTION       OF      MOVEMENT 


FIGURE   10b.      Skipjack  movements  of  75  or  more  miles  as  shown  by  recoveries  of  fish  tagged 
in  1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


TUNA    TAGGING 


335 


GALAPAGOS       ISLANDS 


MALPELO       IS 


COLOMBIA 


SKIPJACK         MOVEMENTS 
TAGGED  IN      NOV.  -  DEC.  -  JAN. 

LEGEND 

WITHIN         SEASON         RECOVERIES 

■• —      DIRECTION       OF       MOVEMENT 


FIGURE    10c.      Skipjack   movements   of  75  or   more   miles  as   shown   by   recoveries   of  fish   tagged 
in  1957  and   1958.  Uncircled  figures  represent  origins  of  the  tagged  fish. 


YELLOWFIN  TUNA  GROWTH 

A  second  objective  of  oiir  tagging  program  was  to  estimate  the 
growth  of  yellowfin  tuna.  Many  fishermen  removed  the  tags  and  sent 
them  in  by  mail.  This  prevented  our  obtaining  complete  recovery  data 
on  all  263  tags  returned  to  us.  Regardless,  we  did  get  complete  data 
on  124  yellowfin  tuna  tagged  off  Baja  California  and  the  Revilla  Gigedo 
Islands,  14  tagged  off  Mexico  and  Central  xVmerica,  19  tagged  off  Peru, 
and  5  from  other  areas.  These  fish,  440  to  990  mm.  fork  length  at  time 
of  tagging  were  at  liberty  for  one  to  842  days.  Detailed  information  of 
individual  tag  recoveries  is  tabulated  in  Appendix  B. 

Baja  California-Revilla  Gigedo  Island  area  data  indicate  that  aver- 
age one-year  growth  rates  for  similar  sized  yellowfin  tuna  were  not  the 
same  for  each  year  of  tagging.  At  time  of  tagging,  size  ranges  of  the 
fish  used  for  growth  analyses  were  440  to  650  mm.  for  1953  tagging, 
585  to  645  mm.  for  1955,  and  500  to  750  mm.  for  tagging  during  1958 
(Table  9).  One-year  growth  rates  were  200  mm.,  420  mm.,  and  350 
mm.  for  1953,  1955  and  1958  respectiveh".  Data  from  the  remaining 
areas  of  tagging  are  not  sufficient  for  annual  growth  rate  determina- 
tion. 


336 


CALIFORNIA  FISH   AND  GAME 


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TUNA    TAGGING 


337 


Data  used  for  growth  analyses  of  yellowfiii  tima  of  the  Baja  Cali- 
fornia-Revilla  Gigedo  Island  area  were  from  recoveries,  through  No- 
vember 30,  1959,  of  fish  tagged  during  1953,  1955  and  1958.  They  were 
from  fish  that  had  been  at  liberty  from  one  to  367  days  (Table  9). 
The  change  in  length  of  each  fish  was  plotted  against  days  at  liberty. 
For  each  year,  a  straight  line  was  fitted  by  least  squares  (Figure  11). 

Regression  analysis,  using  the  method  of  Ostle  (1954),  of  the  growth 
data  was  undertaken  to  determine  if  there  was  a  significant  difference 
between  the  growth  rates  for  1953,  1955  and  1958.  These  tests  showed  a 
significant  difference  {F  =:  11.07;  F oi  ^^,  loo)  =  3.98)  among  the  regres- 
sions and  further  showed  significant  differences  {F  ■=  270.50 ;  i<\„i  (o,  loo) 
=  4.82)  among  their  slopes.  We  conclude  then  that  yellowfin  tuna 
tagged  in  the  Baja  California-Revilla  Gigedo  Island  area  during  1953, 
1955  and  1958  did  not  exhibit  similar  growth  characteristics,  and  should 
therefore  be  treated  separately. 


400  f- 


Y  =  -4  1605  +  0.5590X 
Y=-53  5329  +  I  I489X 
Y=-2I    8035  +  0  9586X 


200 
DAYS 


250  300 

AT     LIBERTY 


400 


FIGURE    11.      Yellowfin  tuna   growth  for  the   Baja   California-Revilla   Gigedo    Island   Area   during 

the  years  1953,  1955,  and  1958. 


338  CALIFORNIA   FISH   AXD  GAME 

Inspection  of  the  growth  curves  reveals  an  apparent  body  length 
shrinkage  graphically  illustrated  where  the  growth  lines  intersect  the 
ordinate.  Exact  values  for  these  intercepts  are  — 4.16  for  1953  taa'ging, 
—53.53  for  1955,  and  —21.80  for  1958  (Table  9).  The  many  varicibles 
involved  in  measuring  fish  at  sea  and  ashore  and  in  body  length  shrink- 
age brought  about  by  freezing  are  the  main  causes  of  this  apparent 
negative  increment.  Loss  in  body  length  due  to  freezing  has  been 
demonstrated  bj'  Godsil  and  Greenhood  (1951).  They  found  that  54 
Hawaiian  j^ellowfin  tuna,  averaging  615  mm.  in  body  length,  lost  an 
average  8.28  mm.  when  frozen  for  four  to  five  weeks.  This  loss  was 
slightly  less  than  determined  in  subsequent  work  by  the  authors. 

Our  one-year  growth  rates  determined  from  1955  and  1958  tagging, 
in  the  Baja  California-Revilla  Gigedo  Island  area,  are  much  the  same 
as  noted  by  Moore  (1951)  from  modal  progression  of  length  frequen- 
cies of  Haw^aiian  tuna  caught  during  1948  and  1949 ;  and  by  Schaefer 
(1959)  from  temporal  progression  of  size  classes  of  Mexican  yellowfin 
tuna  caught  during  1955  and  1956. 

Data  from  our  1953  tagging  reveal  much  slower  growth  than  for  the 
other  two  years  investigated.  This  difference  probably  is  valid,  since 
the  data  agree  with  modal  progression  of  length  frequencies  from  that 
area. 

SUMMARY 

1.  The  California  tuna  industry  is  the  most  important  fishery  industry 
in  the  State.  Yellowfin  tuna  and  skipjack  compose  a  single  fishery 
extending  from  California  to  Chile.  Because  of  the  value  of  the 
fishery  to  the  economy  of  the  State,  the  Department  of  Fish  and 
Game  has  gathered  data  pertinent  to  its  management. 

2.  It  was  felt  that  tagging  offered  the  most  direct  method  of  defining 
the  tuna  stocks  that  support  the  eastern  Pacific  fishery.  The  first 
successful  tuna  tag  was  developed  in  1952  by  investigations  of  the 
California  Department  of  Fish  and  Game.  Wilson  (1953)  reported 
on  results  of  initial  field  trials.  These  trials  demonstrated  that 
yellowfin  tuna  and  skipjack  would  survive  tagging,  and  the  tags 
would  remain  in  place  with  no  apparent  effects  on  the  fish. 

3.  Three  vinylite  tubing  tags,  Types  E,  F,  and  G,  looped  through  the 
flesh  immediately  behind  the  second  dorsal  fin  were  tested  during 
a  field  trial  from  October,  1952  to  April,  1954.  During  this  time, 
4,204  yellowfin  tuna  and  2,839  skipjack  were  tagged.  Based  on  re- 
covery rates,  the  Type  G  tag  was  selected  as  the  best. 

4.  With  the  marketing  of  an  improved  ink  the  protective  outer  jacket 
of  the  Type  G  "spaghetti"  tag  was  removed  in  1956.  An  improved 
yellow  vinylite,  Resinite  X-270-I,  was  used  in  the  construction  of 
all  tags  starting  with  1957. 

5.  Dart  tags  were  field  tested  against  the  Type  G  tag  in  1959.  Skip- 
jack returns  were  in  favor  of  the  dart  tag. 

6.  From  1952  through  1959,  13,213  yellowfin  tuna  and  14,265  skip- 
jack were  tagged  in  the  eastern  Pacific.  Of  these,  263  yellowfin  and 
237  skipjack  were  recovered. 


TUNA    TAGGING  339 

7.  Yellowfin  tuna  and  skipjack  recovered  75  or  more  miles  from  point 
of  tagging  were  used  in  demonstrating  migrations  by  months  of 
the  year. 

8.  Both  yellowfin  tuna  and  skipjack  moved  north  along  the  coast  of 
Baja  California  during  May,  June,  and  July.  By  July  some  fish 
had  started  to  move  south  and  southerly  movements  continued 
through  September  and  October. 

9.  There  was  an  apparent  inte^-change  of  yellowfin  tuna  between  the 
Revilla  Gigedo  Islands  and  Baja  California.  For  skipjack,  however, 
the  movement  was  one  way — from  the  Revilla  Gigedo  Islands  to 
Baja  California. 

10.  Tag  returns  indicated  the  fisheries  off  Baja  California,  the  Gulf 
of  California  and  the  Revilla  Gigedo  Islands  are  supported,  in  some 
degree,  by  yellowfin  tuna  moving  north  along  the  Mexican  coast 
in  winter  and  spring  from  at  least  as  far  south  as  the  Gulf  of 
Tehuantepec,  and  probably  from  as  far  south  as  Central  America. 
This  was  not  found  to  be  true,  however,  for  skipjack. 

11.  Yellowfin  tuna  and  skipjack  did  not  move  between  the  Central 
American  fishery  and  those  off  Peru  and  the  Galapagos  Islands. 
However,  yellowfin  tuna  moved  from  the  Galapagos  Islands  to 
Peru  and  skipjack  moved  from  Peru  to  the  islands. 

12.  Yellowfin  tuna  and  skipjack  traveled  betw^een  the  Gulf  of  Guay- 
aquil and  the  14-Fathom  Bank. 

13.  The  Baja  California-Revilla  Gigedo  Island  area  data  were  sufficient 
for  annual  growth  rate  estimation.  Based  on  tagging,  one-year 
growth  rates  for  j-ellowfin  tuna  440  to  750  mm.  body  length  were 
200  mm.,  420  mm.  and  350  mm.  for  1953,  1955  and  1958  respec- 
tively. 

ACKNOWLEDGMENTS 

Investigations  of  this  type  require  the  whole  hearted  ('fToi-ts  of  ]iiaiiy 
people.  Mr.  Robert  C.  Wilson  instigated  the  program  in  1952  and  the 
first  tags  were  developed  by  Mr.  Edward  C.  Greenhoocl  and  Mr.  Harold 
B.  Clemens.  Since  that  time  the  program  has  been  under  the  direction 
of  a  number  of  people  and  each  contributed  materially.  The  early 
experimental  work  was  conducted  aboard  the  research  vessel  N.  B. 
SCOFIELD  and  sincere  thanks  are  due  Captain  Ivo  Kuselj  and  his 
crew. 

The  lion's  share  of  the  actual  tagging  fell  upon  Pish  and  Game 
Assistants  who  spent  long  and  arduous  hours  at  sea.  Appreciation  is 
also  extended  to  the  skippers  and  fishermen  of  the  tuna  clippers  who 
were  most  co-operative  in  allowing  us  to  accompany  them  to  sea.  Special 
thanks  are  due  Captain  Lou  Brito  and  the  crew  of  the  tuna  clipper 
SOUTHERN  PACIFIC  (now  a  purse  seiner)  who  were  especially  co- 
operative during  six  different  tagging  trips  aboard  their  vessel. 

We  wish  to  acknowledge  the  advice  and  counsel  given  by  Mr.  Nor- 
man Abramson  in  the  statistical  computations  of  the  growth  section. 
Miss  Judith  Cohen  drew  the  charts  and  figures  and  special  thanks  are 
due  her. 


340  CALIFORNIA  FISH   AND  GAME 

LITERATURE   CITED 

Blunt.  C.  E..  Jr. 

1954.  Two  mi(l-P;ifific  recoveries  of  California-tagged  alhacore.  Calif.  Fish  and 
(Jame,  vol.  40,  no.  3,  p.  339. 

Collyei'.  Robert  D. 

1954.  Tagging  experiments  on  the  yellowtail,  Seriola  doisalis  (Gill).  Calif.  Fish 
and  Game,  vol.  40,  no.  3,  pp.  295-312. 

Ganssle,  David,  and  Harold  B.  Clemens 

1953.  California-tagged  alhacore  recovered  off  Japan.  Calif.  Fish  and  Game,  vol. 
39,  no.  4,  p.  443. 

Godsil,  H.  C,  and  E.  C.  Greenhood 

1951.  A  comparison  of  the  populations  of  yellowfin  tuna,  Neotlivnnus  nuicrop- 
tenm.  from  the  eastern  and  central  Pacific.  Calif.  Dept.  Fish  and  Game, 
Fish  Bull.  82.  33  pp. 

Lahr,  Leslie  E..  and  others 

1959.  A  field  study  of  the  relatire  visibility  of  various  colors.  Calif.  Fish  and 
Game,  vol.  45,  no.  3,  pp.  203-215. 

Moore.  Harvey  L. 

1951.  Estimation  of  age  and  growth  of  yellowfin  tuna  (NeofhuniiKS  macrop- 
tenis)  in  Hawaiian  waters  by  size  frequencies.  U.S.  Fi.sh  and  Wildl. 
Serv.,  Fish  Bull.,  vol.  52,  no.  65,  pp.  133-149. 

Ostle,  Bernard 

1954.  Statistics  in  research.  Ames.  Iowa  State  College  Press,  pp.  1.33-137. 

Schaefer.  Milner  B. 

1959.  Report  on  the  investigations  of  the  Inter-American  Tropical  Tuna  Com- 
mission for  the  year  195S.  Inter-Amer.  Trop.  Tuna  C<jmm.,  Ann.  Rept. 
pp.  34-74. 

Shimada,  Bell  M.,  and  Milner  B.  Schaefer 

1956.  A  study  of  changes  in  fishing  effort,  abundance,  and  yield  for  yellowfin  and 
skipjack  tuna  in  the  eastern  tropical  Pacific  Ocean.  Inter-Amer.  Trop. 
Tuna  Comm.,  Bull.,  vol.  1,  no.  7,  pp.  351-421. 

Wilson.  Robert  C. 

1953.  Tuna  marking,  a  progress  report.  Calif.  Fish  and  Game.  vol.  39,  no.  4, 
pp.  429-442. 

Yamashita,  Daniel  T.,  and  Kenneth  D.  Waldron 

1958.  An  all-plastic  dait-tvpe  fish  tag.  Calif.  Fish  and  Game.  vol.  44,  no.  4, 
pp.  311-317. 


APPENDIX 


342 


CALIFORNIA  FISH   AND  GAME 


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to  lO  CD  to  >o  'O  »o  »o  »0  lO  to  lO  CI  CI  CI  CI  C5  CI  CO  CO  CO 

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m  m  mm  m  mmm  m  mmmi  m  mm  m  mi  mi  m  m  m 


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t-i     L.     L^     t-.     L^ 


360 


CALIFORNIA  FISH  AND  GAME 


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TUNA    TAGGING 


361 


APPENDIX  C 

Number  of  Pacific  Yellowfin  Tuna  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Year 


Year  of  release 

Month 
of 

One-degree 

square 

release 

1952 

1953 

1954 

1955 

1956 

1957 

1958 

1959 

28N-118W..- 

Aug 

3 

28N-118W.__ 

Oct 

1 

27N-114W.._ 

Aug 

28 

27N-114W.-. 

Oct 

11 

27N-115W_-- 

Sept 

72 

27N-115W.__ 

Oct 

2 

26N-113W__- 

Aug 

61 

26N-113W^-- 

Oct 

189 

26N-114W_-- 

July 

185 

26N-114W_. 

Aug 

47 

26N-115W___ 

Oct 

64 

25N-110W_._ 

April 

1 

25N-112W___ 

June 

22 

25N-112W_-. 

July 

7 

25N-113W___ 

July 

7 

3 

1 

25N-113W___ 

Aug 

177 

25N-113W_.- 

Sept 

40 

25N-113W.__ 

Oct 

11 

1 

24N-111W___ 

May 

42 

24N-112W_- 

June 

38 

24N-112W___ 

July 

241 

24N-112W___ 

Sept 

5 

190 

23N-111W.^_ 

May 

299 

23N-111W_^- 

June 

45 

99 

23N-111W___ 

July 

104 

7 

23N-111W.-. 

Sept 

153 

23N-112W__^ 

May 

96 

23N-112W___ 

June 

20 

23N-n2W__ 

July 

399 

23N-113\\\-. 

July 

29 

22N-10f)W___ 

Nov 

6 

22N-108W_-_ 

Feb 

'> 

22N-110W. 

May 

5 

22N-110W.-_ 

June 

13 

22N-111W___ 

June 

130 

9 

22N-111W_._ 

July 

160 

22N-112W___ 

June 

75 

22N-112W__- 

July 

44 

22N-n3W,_. 

July 

8 

21N-106W.__ 

Jan 

6 

21N-106W___ 

May 

2 

21N-100W_.. 

June 

43 

18 

21N-106W.-_ 

July 

87 

21N-106W__. 

Nov 

38 

21N-106W_._ 

Dec 

16 

21N-108W__. 

March 

10 

21N-110W__ 

May 

1 

21N-110W___ 

June 

12 

20N-105W_._ 

Nov 

27 

20N-106W__- 

Feb 

1 

20N-100W_„^ 

May 

2 

20N-106W.__ 

June 

1 

84 

20N-106W___ 

July 

6 

20N-106W._^ 

Nov 

12 

20N-107W___ 

March__. 

4 

19N-104W._- 

April 

4 

19N-105W__. 

March 

26 

19N-107W.__ 

June 

3 

19N-111W___ 

July 

1 

19N-111W._. 

Aug 

2 

19N-111W__^ 

Sept 

43 

19N-112W___ 

May 

99 

19N-112W.._ 

June 

15 

19N-112W-__ 

July 

9 

18N-103W... 

May 

43 

18N.103W.-. 

1  June 

1 

6 

■MV2 


CALIFORNIA  FISH    AND  0A:\IE 


APPENDIX   C-Continued 

Number  of  Pacific  Yellowfin  Tuna  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Yeir 


Yeir  of  release 

Month 
of 

(Jnc-degree 

square 

release 

1952 

1953 

1954 

1955 

1956 

1957 

1958 

1959 

1SX-104W___ 

Feb 

7 

18N-104\V... 

March 

2 

18X-104\V__ 

April 

1 

I8N-104\V_._ 

May 

5 

27 

18N-104W_._ 

.lune 

16 

18N-107W_._ 

April 

1 

18N-110\V_.. 

Mav 

13 

18N-111\V___ 

July 

11 

18N-111W__ 

Aug 

1 

18N-111\V___ 

Sept 

50 

18N-n2W___ 

July 

6 

18N-112W___ 

AuK 

1 

18N-114\\\__ 

May 

117 

18N-114\V___ 

June ._ 

120 

8 

60 

17N-101\V___ 

Feb 

67 

27 

17N-101\V___ 

Ai)ril 

26 

17N-101\V._. 

June 

115 

17N-102\V_._ 

Feb 

17 

168 

17N-102\V___ 

March 

3 

17N-102W_.^ 

April 

188 

17N-102W___ 

May 

1 

17N-102W^^_ 

Nov 

15 

17N-103\V___ 

Feb 

39 

17N-103\V... 

March 

8 

17N-103\V___ 

Mav 

10 

17N-104W__ 

Feb 

48 

17N-104\V___ 

May 

2 

17N-10.5W_- 

March 

3 

17N-105\V^_- 

April 

5 

16N-98W 

June 

13 

16N-99W 

Jan 

2 

,   4 

8 

16N-99W 

Feb 

2 

lfiN-99W 

March--. 

39 

16N-99W 

April 

5 

16N-100W_. 

Jan 

18 

2 

16N-100W___ 

Feb 

1 

40 

)riN-100W__. 

March 

6 

16N-100W___ 

April 

3 

1()N-100W__. 

May 

3 

](iN-101\V._^ 

March-.. 

33 

ir.N-101W__ 

April 

15 

ION-101W__. 

Mav 

10 

6 

16N-102W.__ 

Mar-h... 

24 

16N-102W_.- 

April 

7 

1 

16N-103W._. 

.March... 

3 

2 

16N-103W__^ 

April 

1 

15N-94W 

March    _ . 

23 

5 

15N-95W 

Mar-h- _. 

17 

1.5N-9.5W 

May 

18 

1.5N-97W 

Feb 

29 

5 

I0N-97W 

March 

16 

51 

I0N-97W 

April 

77 

15N-98W 

Feb 

20 

1.5N-98W 

March 

40 

15N-98W 

April 

57 

3 

15N-99W 

Feb 

33 

1.5N-99W 

March... 

3 

15N-99\V 

April 

8 

1.5N-99W 

Nov 

10 

loN-100\V_. 

March 

6 

ir)N-101\V_    _ 

March 

31 

loN-102W__ 

March 

5 

14N-92W 

April 

2 

14N-92W 

May 

1 

I4N-93W 

March 

6 

I4N-93W 

April 

7 

TUNA    TAGGING 


86.S 


APPENDIX   C-Continued 

Number  of  Pacific  Yellowfin  Tuns  Taqged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Year 


One-degree 
square 


Month 

of 
release 


14N-93W 

14N-94W 

14N-94W 

14N-95W 

14N-96W 

14N-96W 

14N-97W._- 
14N-97W___ 
14N-98W.__ 
14N-98\V_._ 
14N-100W_- 

i4N-ionv__ 

14N-101W__ 

13N-89W___ 

13N-90W.._ 

13N-90W___ 

13N-91W._- 

13N-92W_^_ 

13N-92W___ 

13N-93W^-_ 

13N-93W__. 

13N-93W___ 

13N-93W___ 

13N-94W___ 

13N-94W_^_ 

13N-9.5W-_. 

13N-9.5W___ 

13N-96W___ 

13N-99W__. 

13N-101W.- 

12N-87W___ 

12N-87W__. 

12N-88W.._ 

12N-88W... 

12N-88W___ 

12N-88W__. 

12N-89W__. 

12N-89W__. 

12N-89W.-- 

12N-89W__. 

12N-90W__. 

12N-90\V__, 

12ISr-90W__. 

12N-90W^. 

12N-91W_. 

12N-91W__, 

12N-91W„_ 

12N-92W... 

12N-92W._. 

12N-93W^_ 

12N-93W._ 

12N-110W_ 

11N-86W_- 

11N-86W.. 

11N-87W.. 

11N-87W.. 

11N-87W__ 

11N-87\V__ 

11N-88W_. 

11N-88W._ 

11N-89\V_ 

11N-89VV__ 

11N-90W__ 

11N-90W_. 

11N-92W_. 

11N-93W.. 


May 

March 

April 

May 

Feb 

April 

Feb 

June 

Feb 

March 

Feb 

Feb 

April 

April 

Feb 

March 

March 

April 

May 

Feb 

Mareh__. 

April 

May 

Feb 

April 

April 

May 

April 

Feb 

Feb 

April 

May___- 
March. . 

April 

May 

Oct 

Jan 

Feb 

March  __ 

April 

Jan 

Feb 

March-  _ 

April 

Feb 

March- _ 

April 

Feb 

March- _ 

Feb 

March- . 

Oct 

Jan 

May 

Jan 

March-- 

April 

Oct 

March-. 

Oct 

March-. 

April 

May 

Oct 

Feb 

Feb 


Year  of  release 


1952 


1953 


1954 


1955 


81 

r.7 


40 


8 
16 


69 


16 
5 

112 
5 


52 


28 


133 


11 
9 


4 
3 

38 
9 


1956 


4 
38 

3 

91 


51 
14 
40 
12 


1957 


1958 


1959 


1 

78 

5 
7 


174 


9 
9 

34 
54 
85 
33 

1 

12 

1 

6 
4 


30 

1 

16 


14 
18 

17 

236 

20 

31 

14 

251 

1 

41 

40 


57 
22 


364 


CALIFORNIA  PISH   AND  GAME 


APPENDIX   C-Continued 

Number  of  Pacific  Yellowfin  Tuna  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Ye^r 


One-degree 
square 


Month 

of 
release 


Year  of  release 


1952 


19.53 


1954 


1955 


1956 


1957 


1958 


1959 


10N-86W 

Jan 

10N-86W 

Feb 

10N-86W 

March 

10N-86W 

April 

10N-86W 

May 

10N-86W 

July 

10N-86W 

Oct 

10N-91W 

May 

10N-109W_.. 

Jan 

10N-109W___ 

Feb 

10N-109W.__ 

May 

10N-109W... 

Oct 

09N-85W 

Jan 

09N-85W 

Feb 

09N-85W 

March 

09N-85W 

April 

09N-85W 

May 

09N-85W 

Sept 

09N-86W 

Oct 

09N-88W 

Oct 

08N-79W 

Feb 

08N-83W 

Feb 

08N-83W 

Oct 

08N-83N 

Nov 

08N-84W 

Jan 

08N-84W 

March 

08N-84W 

Oct 

08N-85W 

March..  _ 

08N-85W 

April 

07N-77W 

Feb 

07N-77W 

April 

07N-78W 

March 

07N-78W 

June 

07N-79W 

Feb 

07N-80W 

Feb 

07N-81W 

Jan 

07N-81W 

March 

07N-81W 

July 

07N-82W 

Jan 

07N-82W 

Feb 

07N-82W 

April 

07N-82W 

July 

07N-83W 

March 

07N-84W 

Jan 

07N-84W 

Feb 

07N-86W 

March 

06N-77W_._. 

Jan 

06N-77W..., 

Feb 

06N-77W 

June 

06N-78W 

March 

06N-78W 

June 

06N-79W 

July 

06N-82W 

March 

06N-83W 

Jan 

06N-84W 

March 

06N-86W 

March 

05N-77W 

Jan 

05N-77W 

Feb 

05N-77W 

March... 

05N-77W 

June 

05N-78W 

Feb 

05N-78W 

March 

05N-80W 

July 

05N-82W 

June 

05N-87W 

Feb 

05N-88W 

Feb 

05N-88W 

March 

139 
12 
37 


37 


48 
6 


23 
0 


12 

89 
o 


14 


27 


18 
2 

6 


1 

1 

f)l 


137 
2 


1 

12 


21 


29 
7 

11 
2 
6 

24 


07 


77 


15 


202 

5 
3 


11 


14 
6 
7 

43 
3 


150 
1 


31 


15 


12 


15 


TUNA    TAGGING 


365 


APPENDIX  C-Continued 

Number  of  Pacific  Yellowfin  Tuna  Tagged  and  Released  by  Area 
(One-Degree  Square),  Montli  and  Year 


One-degree 
square 


04N-78W 
04N-80W 
04N-86W 
03N-81W 
03N-90W 
03N-90W 
02N-78W 
02N-78W 
02N-79W 
02N-79W 
02N-79VV 
02N-79W 
02N-91W 
02N-91W 
01N-79W 
01N-79W 
01N-79VV 
01N-79W 
01N-81W 
01N-90W 
01N-91W 
01N-91W 
01N-91W 
01N-91W 
01N-92W 
01N-92W 
01N-92W 
00N-80VV 
00N-90W 
00N-91W 
00N-91W 
00S-80W_ 
00S-89VV_ 
00S-90W. 
00S-90W_ 
00S-91W_ 
00S-91W_ 
01S-81W_ 
01S-81W_ 
01S-81W_ 
01S-81W_ 
01S-89W_ 
01S-91W_ 
02S-81W- 
02S-81W. 
02S-81W_ 
03S-80W_ 
03S-80W. 
03S-80W_ 
03S-81W_ 
03S-81W_ 
03S-81W_ 
03S-81W, 
03S-81W_ 
04S-81W_ 
09S-79W_ 
09S-79W. 
09S-79W_ 
09S-79W. 
09S-79W_ 
09S-80W_ 
19S-70W_ 
20S-70W. 
20S-70W_ 

Totals... 


Month 

of 
release 


March 
July-. 
Feb.._ 
March 
Feb. . . 
March 

Jan 

May.  _ 

Jan 

Feb. .  _ 
May._ 
Dec... 
March 
Sept... 

Jan 

Feb... 
May.- 
Dec... 
Dec... 
March 
Feb. . . 
March 
Sept._. 
Dec... 
March 
Nov... 
Dec... 

Jan 

March 
Feb... 
March 
March 
March 
Nov... 
Dec... 
March 
April.. 

Jan 

May.. 
July.. 
Dec... 
Nov... 
Nov... 
July.. 
Oct... 
Dec... 
Oct... 
Nov... 
Dec... 

Jan 

April.. 
Oct... 
Nov... 
Dec... 
Oct... 

Jan 

April.. 
Sept... 
Nov... 
Dec... 
Dec... 
Dec... 

Jan 

Dec... 


Year  of  release 


1952 


76 


38 

7 
71 


46 


1.56 
67 


1156 


1953 


14 
60 


472 


12 


1964 


1954 


4 

7 

21 
11 

147 

10 

5 


125 

148 

5 

12 


33 

11 
151 
295 


22 


76 


48 

4 

331 

41 


81 
9 


2195 


1955 


16 


11 


4 
13 

41 


11 
118 


2356 


1956 


581 


1957 


1958 


19.59 


14 


48 


24 


46 
36 


84 

22 

3 

43 

2745 


19 


89 
43 

44 
81 

10 
75 


24 


2110 


106 


866 


CALIFORNIA   PISH   AND  GAME 


APPENDIX   D 

Number  of  Skipjack  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Year 


One-degree 
square 


Moiitli 

of 
release 


Year  of  release 


1952 


1953 


1954 


1955 


1956 


1957 


1958 


1959 


30N-119W__- 

Sept 

28N-115W_-- 

Aug 

28N-116\V__J 

Aug 

28N-121W.__ 

Aug 

27N-114W_._ 

July 

27N-114W__ 

Aug 

27N-114W__- 

Oct 

27N-115W___ 

Sept 

27N-115W__ 

Oct 

27N-I20W_    _ 

Aug 

26N-113W__  . 

June 

26N-113W. 

Aug 

26N-113W_    _ 

Oct 

26N-114W_ 

July 

26N-114\V_    . 

Aug 

26N-115W___ 

Oct 

25N-1I2\V___ 

June 

25N-112W__. 

July 

25N-113W__ 

July 

25N-113W___ 

Aug 

25N-113\V__. 

Sept 

25N-113W___ 

Oct 

24N-111W_-- 

May 

24N-112W___ 

June 

24N-112W___ 

July 

24N-112VV__- 

Sept 

24N-115W..- 

July 

23N-109W___ 

Nov 

23N-111W_-. 

May 

23N-111\V___ 

June 

23N-111W__. 

July 

23N-111W_^_ 

Sept 

23N-112W___ 

May 

23N-112W___ 

June 

23N-112\V__ 

July 

23N-113W_._ 

July 

22N-106W_^_ 

Nov 

22N-106W__ 

Dec 

22N-108\V_-_ 

Feb 

22N-110\V_.. 

June 

22N-niW___ 

June 

22N-111W___ 

July 

22N-112W^._ 

June 

22N-n2\V\__ 

July 

22N-113W___ 

Julv 

21N-105\V__^ 

Nov 

21N-106W___ 

May 

21N-10(5W__ 

June 

21N-106\V^__ 

Nov 

21N-106W___ 

Dec 

21N-110\V_^. 

June 

21N-111\V„^_ 

June 

20N-105\V__. 

Nov 

20N-106W__ 

June 

20N-106W_^^ 

Nov 

19N-106W.__ 

April 

19N-110W__, 

April 

19N-111V\\.^ 

July 

19N-111W_. 

Aug 

19N-112W__^ 

May 

19N-112W___ 

July 

19N-112W_._ 

Aug 

18N-105W._. 

April 

40 
1 

24 
17 

23 


43 


105 


68 


123 
69 


70 
39 

88 
21 
67 


50 
3 


169 

1 
70 


216 

18 
49 


17 

6 

62 

237 

99 


275 

2 

46 

14 

2 

82 
180 

37 

33 

9 


12 


11 
3 

119 


9 
207 

457 
24 

9 

18 

73 

273 


53 
49 


30 

16 


123 
14 


111 


TUNA    TAGGING 


867 


APPENDIX   D-Continued 

Number  of  Skipjack  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Year 


Year  of  release 

]\Iontli 
of 

One-degree 

square 

release 

1952 

1953 

1954 

1955 

1956 

1957 

1958 

1959 

18N-105W,__ 

May 

4 

18N-106W^__ 

April 

38 

18N-107W_._ 

April 

1 

ISN-llOW... 

May 

3 

18N-111W___ 

July 

196 

18N-111W___ 

Aug 

125 

18N-111W__- 

Sept 

1 

18N-112W___ 

July 

73 

18N-112W___ 

Aug 

70 

18N-114W__^ 

May 

7 

18N-114W.-- 

June 

4 

12 

17N-101W__. 

Nov 

1 

17N-103W___ 

May 

2 

5 

17N-104W_. 

April 

2 

16N-100W__ 

May 

29 

16N-101"W\-_ 

April 

4 

16N-101W___ 

May 

21 

17 

lf5N-102W__. 

March 

13 

lGN-102W_-_ 

April 

8 

U)N-102W_.. 

May 

4 

16N-103W___ 

April 

3 

16N-103W^__ 

May 

9 

15N-97W 

March 

8 

15N-98W 

April 

1 

15N-100W._. 

April 

1 

15N-101W_._ 

March- __ 

11 

15N-101W___ 

April 

34 

15N-101W___ 

May 

18 

15N-102W__ 

May 

13 

1.5N-106W_^ 

Feb 

7 

14N-94W 

April 

18 

13N-89W 

April 

9 

13N-90W 

Feb 

2 

13N-90W 

March 

12 

13N-91W 

March 

5 

13N-95W 

April 

45 

13N-96W 

April 

10 

13N-97W_.__ 

Feb 

1 

13N-101W_„^ 

Feb 

2 

12N-87W 

May 

0 

12N-87W____ 

Sept 

73 

12N-88W 

May 

1 

12N-88W 

Oct 

18 

12N-89W 

March 

1 

12N-89W 

April 

6 

12N-90W 

March.  _. 

36 

12N-91W 

Feb 

7 

12N-91W 

April 

1 

12N-92W 

Feb 

37 

12N-93W 

Feb 

5 

8 

12N-93W 

March 

9 

11N-87W 

April 

52 

11N-87W 

Sept 

41 

11N-87W 

Oct 

33 

11N-88W 

Oct 

13 

11N-92W 

Feb 

10 

11N-93W 

Feb 

12 

10N-85W 

Sept 

25 

10N-86W 

Jan 

26 

10N-86W 

Feb 

1 

1 

10N-86W 

March 

16 

4 

10N-86W 

April 

12 

10N-86W 

May 

17 

119 

368 


CALIFORNIA  FISH   AND  GAME 


APPENDIX   D-Continued 

Number  of  Skipjack  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Year 


One-degree 
square 


Montli 

of 
release 


Year  of  release 


1952 


1953 


1954 


1955 


1956 


1957 


1958 


1959 


]0N-86W.__ 
10N-86W_.. 
10N-91W___ 
10N-109W.- 
09N-84W  __ 
09N-85W.__ 
09N-85W„_- 
09N-85W___ 
08N-83W___ 
08N-83W._- 
08N-83W_.- 
08N-84W__ 
08N-85W,__ 
08N-85W___ 
07N-78W__ 
07N-79W_^_ 
07N-81W__^ 
07N-82W_„_ 
07N-82W__- 

07N-82W 

07N-83W___ 
07N-83W___ 

07N-84W 

07N-84W 

07N-85W___. 

07N-86W 

07N-88W__.. 
06N-77W___. 

06N-77W 

06N-78W 

06N-79W 

06N-83W 

06N-83W 

06N-84W 

06N-85W_  _  _ . 

06N-86W 

05N-77W 

05N-77W 

05N-77W 

05N-80W 

05N-82W 

05N-86W 

05N-88W 

04N-88W 

05N-78W 

04N-80W 

04N-81W 

03N-78W 

03N-81W 

03N-90W 

02N-78W 

02N-78W 

02N-79W 

02N-79W 

02N-79W 

02N-79W 

02N-91W 

02N-91W 

01N-79W 

01N-79W 

01N-79W 

01N-79W 

01N-90W 


July__. 

Oct 

May-_- 

Oct 

May_._ 

Feb 

April 

Sept 

Feb 

Oct 

Nov.... 

Oct 

March. 
April... 

June 

Feb.... 

Jan 

Jan 

Feb 

July 

Jan 

March. . 

Feb 

March.. 
March.. 
March. . 

Oct 

Jan 

June 

March.. 

July 

Jan 

June 

March.. 
March.. 
March. . 

Feb 

March,. 

June 

July 

June 

Jan 

Feb 

March-. 

June 

July 

June 

Feb 

March. - 
March,. 

Jan 

May 

Jan 

Feb 

May 

Dec 

March.  . 

Sept 

Jan 

Feb 

May 

Dec... 
March.  • 


42 


3 

25 

50 
11 
55 
1 
20 


13 


23 


10 


10 
24 


20 


10 

3 
6 


11 


3 
21 


112 


15 


10 


2 
58 


17 


3fi 


23 
4 
1 


92 


03 

3 

12 


27 
2 
6 

20 
1 
2 
1 
2 
2 


10 


TUNA    TAGGING 


369 


APPENDIX   D-Continued 

Number  of  Skipjack  Tagged  and  Released  by  Area 
(One-Degree  Square),  Month  and  Year 


One-degree 
square 


Month 

of 
release 


Year  of  release 


1952 


1953 


1954 


1955 


1956 


1957 


1958 


1959 


01N-91W-. 

01N-91W.. 

OlN-91W-_ 

01N-91W_. 

01N-91W_. 

01N-92W.^ 

()1N-92W__ 

00N-80W__ 

00N-89W-. 

00N-90W-- 

00N-90W_. 

00N-91W_. 

00N-91W_. 

00N-91W-- 

00S-80W._. 

00S-80W_.. 

00S-80W._. 

00S-89W_.. 

00S-89W._ 

00S-90W__ 

00S-91W._ 

00S-91W.. 

00S-91W_. 

01S-81W.. 

01S-81W.. 

01S-81W.. 

01S-81W._ 

01S-81W_. 

01S-81W_. 

01S-89W__ 

01S-90W_. 

01S-91W._ 

01S-91W_- 

02S-81W., 

02S-81W,- 

02S-81W.. 

02S-81W._ 

03S-80W-_ 

03S-80W.. 

03S-80W__ 

03S-81W.„ 

03S-81W,_ 

03S-81W__ 

03S-81W._ 

03S-81W._ 

03S-81W._ 

04S-81W_. 

04S-81W.. 

08S-80W_. 

08S-80W.. 

09S-79W_. 

09S-79W_. 

09S-79W__ 

09S-79W., 

09S-79W_. 

09S-80W_. 

09S-80W_ 

11S-78W_ 

19S-70W_ 

20S-70W. 

20S-70W. 


Feb 

March 

Sept 

Nov 

Dec 

March 

Dec 

Jan 

Feb 

March 

Nov 

Feb 

March___ 

Nov 

Jan 

March 

June 

March..  _ 

Dec 

Nov 

March 

April 

Nov 

Jan 

May 

June 

July 

Nov 

Dec 

Nov 

March 

Feb 

March 

May 

July 

Oct 

Dec 

Oct 

Nov 

Dec 

Jan 

Feb 

April 

Oct 

Nov 

Dec 

Feb 

Oct 

April 

Sept 

Jan 

April 

Sept 

Nov 

Deo 

Sept 

Dec 

Jan 

Dec 

Jan 

Dec 


17 
43 

62 


11 


29 
22 


Totals- 


74 


47 
76 


509 


831 


11 
105 

7 

81 
14 


70 
146 


1 
193 

116 


370 


1 

79 

107 

76 


89 

31 

515 

114 

44 

292 
31 


3266 


173 


174 


20 


38 

278 


3 

156 


270 


23 


42 


1010 


39 
94 


2311 


53 

32 

142 

327 

1474 


95 

110 
3 


95 
14 


244 

8 
69 

646 
83 

27 

2 

45 

3401 


14 

106 
1331 


1463 


NOTE 

Toxicity  of  Tricon  Oil  Spill  Erodicator  to  Striped  Bass 

fRoccus  saxafilis) 

Tricon  Oil  Spill  Eradieator  is  a  commercial  product  designed  to 
emulsify  oil  spilled  on  water.  Tlie  manufacturer  lists  the  composition 
as  20  percent  petroleum  sulfonate,  5  percent  fatty  acid  esters,  10  ix-r- 
cent  polyethylene  glycol  ether,  68  percent  petroleum  solvents,  and  2 
percent  alcohol. 

The  use  of  Tricon  Oil  Spill  Eradieator  has  been  proposed  in  waters 
of  the  San  Francisco  Bay  area.  Since  these  waters  are  inhabited  by 
striped  bass,  the  California  Department  of  Fish  and  Game  conducted 
bioassays  in  early  1957,  in  order  to  determine  this  eradieator 's  toxicity 
to  this  species. 

Five  striped  bass  were  placed  in  each  of  eight  aquaria  containing 
7,500  ml.  of  a  mixture  of  water  taken  from  the  San  Joacpiin  Kiver 
at  Antioch  and  various  amounts  of  oil  spill  eradieator.  For  a  control, 
five  bass  were  placed  in  a  ninth  aquarium  with  7,500  ml.  of  river 
v\'ater.  The  bass  used  ranged  from  2.7  to  4.3  inches  and  averaged  3.4 
inches  in  fork  length.  Air  was  bubbled  slowly  througli  the  watci-  in 
;ill  aquaria;  water  temperature  was  maintained  at  apj)roximately  65 
degrees  F. 

The  resultiS  were  as  follows  : 


Percentage 
concentration 

Survival 

of  Tricon 

Oil  Spill 

Eradieator 

Elapsed 
time 

Number  of 
bass  alive 

Remarks 

2.0                 

7  minutes 

0 

All  fish  showed  immediate  distress. 

0.1       

6  minutes 

0 

All  fish  showed  immediate  distress. 

0.05                      -    

8  minutes 

0 

All  fish  showed  immediate  distress. 

0.005             -        -    --- 

30  minutes 
1  hour 

2 
0 

All  fish  showed  distress  after  about  one 

minute. 

0.0016       

1  hour 

2  hours 

3  hours 

4  hours 

5  hours 

5 
3 
2 
1 
0 

Fish    started    showing    irritation    after 

several  minutes. 

0.001                        

4  hours 

5  hours 

6  hours 

8  hours 

9  hours 
10  hours 

5 
3 

2 
2 
1 
0 

Fish  showed  first  signs  of  distress  at  1 V^ 

hours. 

0.0005         ^    

48  hours 

5 

Fish  showed  no  distress. 

0.0005                 -    

48  hours 

5 

Fish  showed  no  distress. 

Control 

48  hours 

5 

Fish  showed  no  distress. 

(371) 


372  CALIFORNIA  FISH   AND  GAME 

These  results  sliow  clearly  that  Tricon  Oil  Spill  Eradieator  is  toxic 
to  striped  bass  at  low  concentrations.  It  is  probable  that  lethal  con- 
centrations would  Occur  at  least  locally,  if  the  eradieator  were  used 
to  treat  oil  spills. — Harold  K.  CJiadwick,  Californid  Dept.  of  Fish  and 
Game,  January,  1960. 


NOTE 

A  Range  Extension  of  the  California  Halibut 
(Parolichthys  californicus) 

On  Xoveinber  10  or  11,  1959,  Mr.  Jim  Riley,  skipper  of  the  trawler 
IN  A,  was  fishing  for  English  sole  (Parophrys  vefidus)  and  petrale 
sole  (Eopsetia  jordani)  in  30  to  35  fathoms  of  water  four  to  six  miles 
north  of  Redding  Rock.  While  sorting  liis  eatch,  he  discovered  a  fish 
he  believed  was  a  California  halibnt.  He  turned  it  over  to  me  and 
asked  me  to  verify  his  identification. 

It  was  taken  to  Eureka  Marine  Resources  Laboratory  where  positive 
identification  was  made  (counts  and  measurements  are  listed  in  Table 
1).  This  proved  a  substantial  northerly  extension  of  the  previous  known 
range,  Tomales  Bay  (Roedel,  1953). 

TABLE  1 

Meristic  Counts  and  Measurements  From  a  Left-eyed  Paralichfhys  californicus  Taken  Off 

Redding  Rocl<,  November  1959 

Measurements  :* 

Standard  length 370 . 0 

Total  length 116.2 

Head  length 19.9 

Snout  length 5.7 

Orbit  width 2.7 

Maxillary  length 10.5 

Body  depth 41.1 

Counts: 

Dorsal  rays 72 

Anal  rays 56 

Ventral  rays :  right 6 

left -.  6 

Pectoral  rays :  right 12 

left 12 

Principal  caudal  rays 17 

Gill  rakers :  lower  limb 20 

upper  limb 9 

*  Standard  lengtli  given  in  millinii'tci-s;  all  other  mpasiiicmciits  presented  as  pci-eenfaKPS  of  staiidaifl  leiiclli. 

A  California  halibut  was  reported  from  this  area  on  Januaiy  23, 
1952,  when  a  fish  and  game  warden  told  biologist  R.  B.  McCormick 
one  had  been  caught  by  the  trawler  DOliOTlIY  AXX  off  the  mouth  of 
the  Klamath  River.  This  was  confirmed  by  Ray  Hamblock,  manager 
of  the  Balesteri  Fish  Company.  He  stated  that  the  fish  weighed  24 
pounds.  It  was  no  longer  available  so  McCormick  could  not  make  a 
positive  identification. 

On  August  30,  1954,  while  making  a  sportfish  survey  at  Buhne's 
Point  (Humboldt  Bay),  McCormick  recorded  a  California  halibut  that 

(  373  ) 


31i  CAUFOENIA  FIBH  ASD  GAME 

liad  been  taken  by  a  BportKiaan  wlule  drift  fishijig  for  salmon  at  the 
moutb  of  the  bar.  Positive  identifieatioB  -wa*;  made  bj  MeCormiek. 
MeaKurementK  and  fin  coiint«  -wrere  taken^  but  iinfortimatejT  tM«  in- 
formation wa«  loKt  ri"--'_r  a  move,  ""i  '^'.  - -f'  ■'i  -  -f'  i  -  m  file  at  tli€ 
Eureka  laboratory  jj  ■•  it  wan  aj  ^  .      _  -  long. 

On  AugTiKt  15,  1959,  biologist  Dan  (jotsbaU  was  ijiform-ed  by  a  sports- 
fisherman  that  a  California  halibut  had  been  taken  at  Shelter  CoT-e 
(Humboldt    County).    GotshaU    contacted    tbe    fishermen     fKalph    L. 
Reese),  but  the  fish  was  not  arailable  so  Mr.  E.eese  sent  photos  to  sub- 
stantiate the  Talidity  of  the  report. 

REFERENCE 
Koedel,  Phi]  M. 

1953.  CommoD  ocean  fishes  of  the  CaliforuLia  eoa«t.  Calif.  I>ept.  Fi«h  and  'Gaine, 
Fish  Bun.  91,  184  pp.,  175  fig«. 

E.  <?.  'Cht.nderson,  Marine  Eenowroes  •Operations,  'California  Depuriineni  of  Fish 
and  Ganoe,  Janua/ry,  1960. 


REVIEWS 

Oceanography  and  Marine  B'.ology 

By  II.  I'.ai'iics;  The  M;icinillaii  (\...  New  York.  I!).".'.! ;  21S  pp..   I  HI  li-s.  :•,.".  sliillinns. 

This  is  a  l)(H)k  of  l<H'hiii(HU's.  It  is  (k'siiiucil  to  inforiu  the  i-cadcr  liow  l^iiow  led;;!' 
of  the  sea  and  of  some  of  its  iiihahitaiits  is  ohtaiiu'd.  It  is  wfitti'ii  in  ,i  siinpif 
straightforward  style  inakinj;-  it  easy  for  a  li('?;iiinci-  to  dcridr  wliai  insi  rnnifuls 
lua.v   best  suit  his  needs. 

.\  primary  coiieerii  is  witii  liic  prolilcnis  imnlxcd  in  iiiai^iiii;'  oliscr\  al  ions  and 
ineasui'ements  in  the  oeean.  Tliis  is  one  of  the  few  times  that  the  scattered  accounts 
of  etiuipment  and  techni(pH's  used  in  oceanojiraphy  au<l  uuirine  hiolo<;y  have  hccu 
assemiiled  under  one  co\'er — this  ah>ne  makes  the  booli  a  welcome  addilion  In 
tin'    literature. 

A  hook  of  this  sco|)e  necessarily  involves  faii'ly  detailed  descriptions  of  f;'eai' 
and  methods;  suiijects  that  ordinarily  make  dull  readinj;-  for  all  except  the 
professional  worker.  l>r.  Barnes  sm-eeeds  in  holding;  the  reader's  interest,  however, 
by  frequently  insert  ini;  into  the  gear  descriptions  discussions  of  applications,  results, 
and   limitations;   and   by   the  lil)(»ral   use  of  drawings  and   photographs. 

It  resendiles  a  hamlbook  and  is  divided  into  four  nni.jor  sections:  the  tirsi  deals 
with  nu'thods  and  gear  used  for  sampling  living  pidagic  organisms,  except  fish, 
and  those  that  live  on  and  within  the  ocean  bottom  sedinu'uts;  the  second  section 
describes  the  use  of  shijjboard  sound  waves  in  relation  to  lisheries,  and  includes 
a  disc'ussi(ni  of  umlerwater  noises  pi'oduced  by  \ai-ious  sitecies  of  lish  ;  the  third  is 
concerned  with  proi)erties  of  the  water  itself,  but  is  limited  to  temperalnre,  -alinity, 
and  current  measnrments ;  and  the  l.-ist  section  rel.-ites  both  aerial  and  underwalei- 
photogra]ih.\-   to  tisheri<>s   problems. 

Dr.  r.arnes  also  has  included  nine  pages  of  ret'eienees.  which  will  piove  of  con- 
siderable v;ilue  to  anyone  interested  in  oceanography  and  marine  bi(dogy  t  eelin  iipu's. 
—  JTdidhJ    II.   Clciiifiis.   CdHfuriiid    I  hp<i  rhiicii  t   (if   Fisli    diiil   fhniir. 

Nafural  Resources 

By   INIartin    K.   Iluberty   ami   Warren   L.   Flock;   IMcGra w  1  lill   Book   Company.    Inc., 
New    York.    I'.ir.'.l;    xviii  -t-  nr.n  p]).,   $11. 

This  book  was  wi'itten  as  a  textbook  in  natni-al  resoni'ces  study  for  use  by 
engineering  students  at  the  university  level.  As  snch,  it  compiles  within  its  ."."it;  pages 
a  tremendous  wealth  of  knowledge  and  |irof(Min(l  thought  regarding  both  nnr  renew- 
al)le  and  nonrenewable  resources. 

Leading  authorities  have  eadi  wi-itten  dnipters  covering  their  respective  lields. 
l^xamples  are:  Marine  Resources.  MiliH'r  Sdmefer  ami  Roger  Heville  ;  Ecolog.v  and 
Wildlife,  Walter  P.  Taylor;  ami  Forest  Land  and  Forest  Products,  John  .\. 
Zivnuska. 

The  chapter  on  marine  resources  is  of  especial  interest  to  biidogists.  All  uses  of 
the  ocean  environnu-nt  are  considered  from  recreation  and  waste  disjjo.sal  to  water 
supply.  Emphasis  is  placed  <m  the  fact^  that  we  currently  harvest  oidy  a  small 
fraction  of  the  organic  production  of  the  sea. 

"The  challenge  of  new  fields  to  cinnpuM-  is  clearly  shown  when  we  consider  that 
the  ma.jor  fisheries  are  for  the  same  kiml  of  organisms  that  ha\e  been  exploited  since 
man  first  went  to  sea,  that  is,  those  whose  aggregation  habits  make  Ibeni  amenable 
to  lai-ge  scale  capture  by  the  tradition.-il  kinds  of  gear." 

Regarding  human  consumption  of  marine  food  pnxlucts,  it  was  surprising  to  learn 
that  in  the  United  States  it  has  not  in<re,ised  <ni  a  pei-  c.ipita  basis  during  the  i)ast 
20  years  despite  improved  refrigeration,  transportation  ami  retail  marketing  facili- 
ties. (%'i-tain  specific  marine  food  items  ha\'e  increased,  bni   ,it    the  exjiense  of  others. 

The  author  does  not  anticipate  the  use  of  lower  levids  of  the  marine  food  chain  to 
be  economically  pidtitable  for  many  years.  A  similar  prognostication  is  made  for 
farming  the  sea  in  a   manner  analogous  to  agriculture  excepi    for   the  shellfish. 

(375) 


376  CALIFORNIA  FISH  AND  GAME 

Many  sage  comments  are  fniiiul  throughout  the  book  sut-h  as  this  one:  "There  is 
a  vory  groat  ueetl  for  thorough  studies,  coniluuing  ecoiuuuios  and  the  natural  sciences 
of  marine  resources  in  (•r(h'r  In  (h'vtdop  a  ni()re  rational  hasis  for  their  exploitation." 

Other  chapters  ar(>  eiiually  informative.  The  biologist  as  well  as  the  physical 
scientist  will  find  this  volume  most  useful  as  a  means  of  broadening  his  background 
informal ii)n  on  our  natural  resources  and  their  uses.  It  will  serve  also  as  a  handy 
reference. —  Willis   A.   Kraiis.  ('(ilifurnin   T)r]iiirl mi  ul  of  Fish   (i)iil  (liniiV. 


prhileJ  ill  caiitornm  STATn  PRiNTiNfi  oi'fice 
17250      4-00      5,200 


1